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Jennifer’s Post
I had a difficulty finding non-reactive studies for the particular
research that I have been focusing on. The first one that I found
seems to be both reactive and non-reactive. People were
involved in the first portion of the study, but were not aware of
the second phase. The first academic journal that I found is
titled “Does Counting Emotion Words on Online Social
Networks Provide a Window into People’s Subjective
Experience of Emotion? A Case Study on Facebook. Content
analysis was used to determine if the words that people post are
linked to how they really feel. Reactive measures were used
first to question participants on how they felt during the week.
Word counting algorithms were used to determine if people
really feel the way that they portray on social media. Four
samples were used for the study. Facebook data and experience
surveys were used to determine if emotion words can be linked
to somebody’s true emotional status. The multi-level data
analysis included four phases. It was found that there is not a
link between a person’s emotions and the words that they post
on social media. (Kross, et al., 2019)
The second article that I found is titled “Objectifying Fitness: A
Content and Thematic Analysis of #Fitspiration Images on
Social Media. Non -reactive measures were used to determine if
the large volume of #fitspiration posts on Instagram are linked
to body dissatisfaction. Hashtags such as #fitspiration were
analyzed in terms of body types and how the posts were
presented. The purpose is to find the link between the images
and the theory of objectification. It theorizes the dangers of
women being bombarded by what is considered an ideal body
type. The first question that was asked was "What are the most
common types of imagery featured in #fitspiration posts on
Instagram?” (Deighton, Bell, 2018). The posts were coded into
categories such as body type, body proportion, pose and
clothing type. It was found that the majority of the posts depict
thin people with low body fat. In a second study that used
content analysis the themes of #fitspiration was looked at. In
both studies objectification theory was seen. In both studies,
thinness is linked to beauty in unrealistic ways that can be
detrimental to peoples body image. For me, finding non-reactive
studies were difficult. Many of the articles that I found included
surveys as the primary measure, or both reactive and non-
reactive measures. This makes me think that it could be difficult
to gain physical evidence regarding social media usage without
violating privacy or other ethical concerns.
References
Deighton-Smith, N., & Bell, B. T. (2018). Objectifying fitness:
A content and thematic analysis of #fitspiration images on
social media. Psychology of Popular Media Culture, 7(4), 467–
483. https://doi.org/10.1037/ppm0000143
Kross, E., Verduyn, P., Boyer, M., Drake, B., Gainsburg, I.,
Vickers, B., Ybarra, O., & Jonides, J. (2019). Does counting
emotion words on online social networks provide a window into
people’s subjective experience of emotion? A case study on
Facebook. Emotion, 19(1), 97–107.
https://doi.org/10.1037/emo0000416.supp (Supplemental)
Paul’s Post
Articles:
McKibben, W. B., Umstead, L. K. & Borders, L. D. (2017).
Identifying dynamics of counseling Leadership: A content
analysis study. Journal of Counseling & Development, 95(2),
192–202. https://doi.org/10.1002/jcad.12131
Burbank, M., Odom, S. F., & Sandlin, M.R. (2015). A content
analysis of undergraduate students’ perceived reasons for
changes in personal leadership behaviors. Journal of Leadership
Education, 14(2), 182–197. https://doi.org/10.12806/V14/I2/R12
Textbook:
Neuman, W. L. (2017). Understanding research. New York, NY:
Pearson.
Topics:
The first article chosen discusses the relationship between
leadership and counseling. The study wanted to seek "how
counseling leadership works as a social dynamic by identifying
the content and processes involved" (McKibben et al., 2017).
Many components across leaderships theories emerged such as
positive reinforcement and mentorship.
The second article reviewed seeks to help change leadership for
undergraduates after they have taken a course in leadership
practices. "Individuals learn and develop leadership through a
variety of mediums such as formal coursework, youth and
collegiate programs, educational experiences, and on-the-job
experiences" (Brungardt, 1997; Cress, Astin, Zimmerman-Oster,
& Burkhardt, 2001; Dugan, 2006). "Understanding the link
between leadership development and leadership education is
essential as leadership educators attempt to expand the
capacities of individual students in the classroom through
curricular activities and outside the classroom through co-
curricular assignments"
Article findings:
Article one:
"On the basis of a systematic coding procedure, we identified 24
themes that described leadership dynamics in the counseling
profession (Research Question 1), which were then grouped by
commonalities into three broad categories (Research Question
2)" (McKibben et al., 2017). The researchers used content
analysis by using "an inductive coding approach to allow
themes to emerge without the constraints of an a prior
theory" (Krippendorff, 2013). Full length articles were used
from counseling journals. An inductive approach was used in
order for them to randomly select two articles as a pretest.
Article two:
The article wanted readers to know that a Student-Leadership
Practices Inventory was conducted. This was a pre/post
assessment. Students must be enrolled in a leadership course,
needed to complete the student inventory, and respond to
reflection prompts. The class used the Kolb's Experimental
Learning Model to reflect on their changes in leadership
qualities. This study used content analysis which is a
"nonreactive technique that lets you examine both hidden and
visible content in communication messages" (Neuman, p. 163,
2017). Specifically, the researchers used the instructors for the
course. In order to prevent potential bias in results, "the
analysis of the student reflections and consent to participate in
the study was not conducted until the conclusion of the course.
As another way to limit bias, names were removed and
reflections were coded by someone other than the instructor
before analysis was conducted" (Burbank, M., Odom, S. F., &
Sandlin, M.R. (2015).
Made you think:
The articles that I chose made me reflect in a few ways with
regards to nonreactive measures. First, finding articles that
relate to your topic is important. Narrowing down what it is
specifically want you want to research is key to maintain
direction. To help guide in a content analysis there is an eight
step process. To name two portions in our steps would be
identify text to analyze and decide on units of analysis. A
coding system using leadership theory would be sufficient for
my research proposal. "You must tailor the coding system to the
specific type of text or communication medium you are
examining, such as television dramas, novels, music videos,
photos in magazine advertisements, and so forth" (Neuman, p.
164, 2017). Then I must break down to the unit of analysis, such
phrases for leaderships would be "coaching," leaderships" and
"mentor".
A healthy building is based on the successful
fulfillment of many requirements. For each
building, sound design and construction are
necessary for its technical functioning and
mechanical stability and for the basic safety of
its occupants. However, this is not sufficient to
ensure indoor environmental quality (IEQ) for
its occupants. There are a number of other fac-
tors that affect the occupants’ well-being either
directly or indirectly. Among such factors are
heating, ventilation and air conditioning, and
activities of the occupants, including the use of
office equipment or household activities such
as cooking, cleaning, or applying pesticides.
The risk assessment of indoor contaminants
and the effectiveness of interventions are chal-
lenges faced globally because of vast differences
in the types of residences and their climates as
well as the many types of household products,
furniture, appliances, and so on, that are avail-
able to consumers today. Examples of these
diverse challenges have been demonstrated in
the book The Material World that provides
detailed, thought-provoking visual and written
portraits of “statistically average” families and
their households in 30 nations around the
world (Menzel 1994).
Indoor air pollution is not a new problem,
although only recently has it become a matter
of public concern. As early as the 18th century,
hygienists had identified the consequences of
inadequate ventilation in the indoor environ-
ment. Systematic research activities emerged
soon after World War II, in some respects
reversed by energy conservation measures intro-
duced in housings after the oil crisis in the early
1970s. Since then, the complexity and the
health relevance of the indoor environmental
problem have become increasingly apparent
(European Commission 2005a, 2005b).
Failures to control indoor air risks have
huge economic consequences in the form of
health care costs, lost working days, and per-
sonal costs to individuals (Mendell et al. 2002).
Consequently, investments in developments
that pursue enhanced human health and well-
being through healthier indoor environments
should not be seen as business nuisances but
should be weighed against the benefits gained.
Because factors contributing to building health
are complex, with connections to many essential
fields, we do not attempt to cover all aspects but
present three essential ideas: sustainable develop-
ment of buildings and communities, the effect
of occupants on the indoor environment, and
recent developments in creating healthier prod-
ucts and building materials with a focus on
moisture and mold control. These three areas
are important because they address the most
current issues in building design: sustainability
(in terms both of natural resources and of the
lifetime of the building); individual behaviors
and how they affect their indoor environments;
and the newest trends in building materials that
can promote healthier indoor environments.
Environmental Sustainability
Contributes to Health,
Productivity, and Quality of Life
Sustainable design is a collective process
whereby the built environment achieves eco-
logic balance in new and retrofit construction
toward the long-term viability and humaniza-
tion of architecture. In an environmental con-
text, this process merges the natural, minimum
resource-conditioning solutions of the past
(daylight, solar heat, natural ventilation) with
the innovative technologies of the present into
an integrated “intelligent” system that supports
individual control to achieve environmental
quality with resource consciousness. Sustainable
design rediscovers the social, environmental,
and technical values of pedestrian, mixed-use
communities, fully using existing infrastruc-
tures, including “main streets” and small-town
planning principles and recapturing indoor–
outdoor relationships. It attempts to avoid the
thinning out of land use and the dislocated
placement of buildings and functions caused by
single-use zoning. Sustainable design introduces
benign, nonpolluting materials having lower
operating energy requirements and higher
durability and recyclability. Finally, sustainable
design offers architecture of long-term value
through modifiable building systems through
life-cycle instead of least-cost investments and
through timeless delight and craftsmanship
(Loftness et al. 2005).
The importance of proving that sustain-
able design and engineering improves health,
productivity, and quality of life has never
been more important. To this end, the
Center for Building Performance at Carnegie
Mellon University in collaboration with the
Advanced Building Systems Integration
Consortium (ABSIC) from 2000 to the pre-
sent have been developing a building invest-
ment decision support tool—BIDS (Carnegie
Mellon, Pittsburgh, PA). This cost–benefit
tool presents the life-cycle data of over
Environmental Health Perspectives • VOLUME 115 | NUMBER
6 | June 2007 965
Research | Mini-Monograph
This article is part of the mini-monograph “Developing
Policies to Improve Indoor Environmental Quality.”
Address correspondence to A. Nevalainen, Neulanie-
mentie 4, FI-70700 Kuopio, Finland. Telephone: 358
17 201 342. Mobile: 358 400 587 634. Fax: 358 17
201 155 E-mail: [email protected]
The authors declare they have no competing
financial interests.
Received 9 January 2006; accepted 25 January 2007.
Elements That Contribute to Healthy Building Design
Vivian Loftness,1 Bert Hakkinen,2 Olaf Adan,3 and Aino
Nevalainen 4
1Carnegie Mellon University, School of Architecture,
Pittsburgh, Pennsylvania, USA; 2Gradient Corporation,
Cambridge, Massachusetts,
USA; 3TNO Built Environment and Geosciences, Delft, the
Netherlands; 4National Public Health Institute, Department of
Environmental
Health, Kuopio, Finland
BACKGROUND: The elements that contribute to a healthy
building are multifactorial and can be
discussed from different perspectives.
OBJECTIVES: We present three viewpoints of designing a
healthy building: the importance of sus-
tainable development, the role of occupants for ensuring indoor
air quality, and ongoing develop-
ments related to indoor finishes with low chemical emissions
and good fungal resistance.
DISCUSSION: Sustainable design rediscovers the social,
environmental, and technical values of
pedestrian and mixed-use communities, using existing
infrastructures including “main streets” and
small-town planning principles and recapturing indoor–outdoor
relationships. This type of design
introduces nonpolluting materials and assemblies with lower
energy requirements and higher dura-
bility and recyclability. Building occupants play a major role in
maintaining healthy indoor envi-
ronments, especially in residences. Contributors to indoor air
quality include cleaning habits and
other behaviors; consumer products, furnishings, and appliances
purchases, as well as where and
how the occupants use them. Certification of consumer products
and building materials as low-
emitting products is a primary control measure for achieving
good indoor air quality. Key products
in this respect are office furniture, flooring, paints and coatings,
adhesives and sealants, wall cover-
ings, wood products, textiles, insulation, and cleaning products.
Finishing materials play a major
role in the quality of indoor air as related to moisture retention
and mold growth.
CONCLUSIONS: Sustainable design emphasizes the needs of
infrastructure, lower energy consump-
tion, durability, and recyclability. To ensure good indoor air
quality, the product development for
household use should aim to reduce material susceptibility to
contaminants such as mold and
should adopt consumer-oriented product labeling.
KEY WORDS: consumer products, dampness, emissions, fungal
resistance, healthy buildings, indoor
air, sustainable development, ventilation. Environ Health
Perspect 115:965–970 (2007).
doi:10.1289/ehp.8988 available via http://dx.doi.org/ [Online 25
January 2007]
200 case studies—laboratory, field, and simu-
lation studies that reveal the substantial envi-
ronmental benefits of a range of advanced and
innovative building systems. The health bene-
fits of high-performance buildings designed to
deliver high-quality air, thermal control, light,
ergonomics, privacy, and interaction as well as
access to the natural environment were ana-
lyzed (Center for Building Performance and
Diagnostics/Advanced Building Systems
Integration Consortium 2005). The following
components were included:
• healthy, sustainable air;
• healthy, sustainable thermal control;
• healthy, sustainable light;
• workplace ergonomics and environmental
quality;
• access to the natural environment; and
• land use and transportation.
Healthy, sustainable air. This component
depends on commitments to improve the qual-
ity and quantity of outside air, maximize nat-
ural ventilation with mixed-mode heating,
ventilating, and air-conditioning (HVAC) sys-
tems, and separate ventilation air from thermal
conditioning, provide task air and individual
control, and improve pollution source control
and filtration. International case studies have
demonstrated that high-performance ventila-
tion strategies reduce respiratory illness 9–20%
and increase individual productivity between
0.48 and 11%, with a small energy cost for
increasing outside air rates with heat recovery,
or 25–50% energy savings for natural ventila-
tion and mixed-mode conditioning (e.g., Fisk
and Rosenfeld 1997; Kroeling et al. 1988).
Healthy, sustainable thermal control. This
second component depends on commitments
to separate ventilation air from thermal condi-
tioning, design for dynamic thermal zone size,
provide individual thermal controls (e.g.,
underfloor air), design for building load balanc-
ing and radiant comfort, and engineer proto-
typed, robust systems. International case studies
demonstrate that providing individual tempera-
ture control for each worker increases individ-
ual productivity by 0.2–3% and reduces sick
building syndrome (SBS) symptoms and absen-
teeism, while saving 25% of conditioning
energy (e.g., Wyon 1996).
Healthy, sustainable light. The third com-
ponent can be achieved by maximizing the use
of daylight without glare, selecting the highest
quality lighting fixtures, separating task and
ambient light, and designing plug-and-play
lighting with dynamic lighting zones. Case stud-
ies demonstrate that improved lighting design
increases individual productivity between 0.7
and 23%, reduces headaches and SBS symp-
toms by 10–25%, while reducing annual energy
loads by 27–88% (Heschong et al. 2002).
Workplace ergonomics and environmental
quality. Improving this fourth component has,
as its goals, the well-being and efficiency of indi-
vidual workers with energy-efficient technolo-
gies; optimal lighting, temperature, and
placement of furniture; and healthy interior
materials. Sustainable design depends on the use
of materials that support healthy environments
while reducing transportation energies that carry
secondary health concerns. Material selection is
critical to thermal performance, air quality and
outgassing, toxicity in fires, cancer-causing
fibers, and mold, all which affect respiratory and
digestive systems, eyes, and skin (Dainoff 1990).
Access to the natural environment. The fifth
component is achieved by providing individual
access to nature by maximizing the use of day-
light without glare, maximizing the use of nat-
ural ventilation with mixed-mode HVAC, and
designing for passive solar heating and cooling.
Access to the natural environment may increase
individual productivity between 0.4 and 18%
and reduce absenteeism, SBS, and recovery
time while saving even 40% of lighting energy
(Center for Building Performance and
Diagnostics/Advanced Building Systems
Integration Consortium 2005).
Land use and transportation. This last
component can be improved by commitments
to designing mixed-use communities, allowing
for multigenerational mobility with mixed-
mode transportation, and preserving and cele-
brating natural landscapes. For land use,
walkable neighborhoods may contribute to
prevention of obesity (Srinivasan et al. 2003).
Cool roofs and cool community developments
with increases in landscaped surfaces and tree
canopies demonstrated reductions in annual
cooling loads by 10%, peak cooling by 5%, as
well as benefits for carbon sequestration, storm
runoff management, and a 6–8% reduction in
smog that could potentially reduce respiratory
illnesses (Rosenfeld and Romm 1997).
Quantifying the Value of the
Built Environment to Health
It is imperative to incorporate the full life-cycle
costs of a poor-quality built environment, from
materials to systems to land use and transporta-
tion. Based on health insurance costs reported
in five references by independent nonprofit
organizations, human resource research firms,
and the U.S. government, the average employer
cost for health insurance was approximately
US$5,000 per employee per year in 2003
(Figure 1). Some health conditions and illnesses
have been linked to the quality of the indoor
environment, including colds, headaches, respi-
ratory illnesses, musculoskeletal disorders, back
pain, and symptoms of SBS. These are pre-
sented in Figure 1 with references.
Suboptimal indoor environments can lead
to a variety of adverse health effects that result
directly in increased physician visits and medical
treatment. This leads to increases in health
insurance costs, both for institutions and for
individuals. Improvements in indoor environ-
ments, such as increased ventilation rates, better
ergonomics and lighting, and improved heating
and cooling methods, would reduce many of the
adverse symptoms and illnesses described above.
Human health in the built environment is
one of the most critically needed research efforts,
requiring both extensive experimental and field
research. Controlled laboratory experiments
Loftness et al.
966 VOLUME 115 | NUMBER 6 | June 2007 • Environmental
Health Perspectives
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40,000
35,000
30,000
25,000
20,000
15,000
10,000
5,000
0
Chumu
($200)
FMr
($412)
Energys,t
($450)
Rent/mortgageq,r
($3,200)
Technology
($10,000)
Benefitsa,b
($18,500)
Salarya,b
($45,000)
Potential benefits of quality buildings
$5,300 Turnoveri,j
$765 (1.7%) Absenteeismk
Worktime
loss
$5,000 Healthc–g
$244 Lower respiratoryl
$101 Asthmam
$95 Allergiesm
$92 Back painn
$73 Headachesm
$68 Coldo
$17 MSDp
$19 Throat irritationm
$18 Eye irritationm
$18 Sinus conditionsm
$1,000 Connectivity
(Forrester Group)
$226 Interior systems
$70 Utility central systems
$62 Roads and grounds
$36 External building
$73 Process and
environmental systems
12.5%
Productivityh
Figure 1. Improving the quality of the built environment will
reduce the life cycle costs of business.
Monetary amounts are in U.S. dollars per year. MSD,
musculoskeletal disorders. Forrrester Group is part
of Forrester Research (Cambridge, MA).
Data from aU.S. Department of Labor (DOL) (2004a); bU.S.
DOL (2004b); cU.S. DOL (2002); dKaiser Family Foundation
and Health
Research and Educational Trust (2003); eTowers Perrin HR
Services (2003); fU.S. Chamber of Commerce (2003); gDeloitte
&
Touche (2003); hLeaman (2001); iU.S. DOL (2003b); jFitz-Enz
(2000); kU.S. DOL (2003a); lBirnbaum et al. (2003); mU.S.
EPA (1998);
nGuo et al. (1999); oFendrick et al. (2003); pSilverstein et al.
(2000); qGeneral Services Administration (2003); rInternational
Facility Management Association (IFMA) (2002); sU.S. DOE
(1998); tU.S. Department of Energy (DOE) (2004); uIFMA
(2001).
need to be carried out simultaneously with
experiments in actual buildings to map chains of
consequence and to identify possible building-
related causes for the rise in respiratory prob-
lems, fatigue, stress, depression and other
health-related declines in the quality of life. Yet
there is remarkably little federal investment in
defining and valuing healthy buildings and
communities (Figure 2).
The opportunity to substantially improve
the health of building and community resi-
dents through investments in higher quality
materials, systems, and land-use planning is
significant. The catalyst for these investments
must be research and subsequent policy based
on the combined expertise of the health
research community and the sustainable
design and engineering disciplines that we
hold responsible for our built environment.
Human Influence on Healthy
Indoor Air
Humans have a major role in maintaining the
quality of the indoor environments in which
they live. Lifestyles that affect IEQ include the
following:
• Personal cleaning habits. Examples include
frequency of vacuuming and washing of bed
linen and towels.
• Other personal behavior such as whether
kitchen or bathroom fans are commonly used
and whether windows are opened to increase
air circulation if certain consumer products
are used.
• The types of consumer products that are pur-
chased and where and how the consumer and
other occupants of the residence use them.
• Decisions about the types of house or apart-
ment furnishings that are purchased, for
example, the presence of carpets and curtains
in various rooms, and remodeling choices.
• Decisions about the types of appliances that
are purchased, for example, a central air
cleaning system or a high-efficiency vacuum
cleaner.
• Personal cleaning habits.
Examples of the sources of indoor pollu-
tants such as lead, pesticides, polycyclic aro-
matic hydrocarbons (PAHs), allergens, and
volatile organic compounds (VOCs) include
consumer products, the dust present in carpets
and furniture, household pets, or pollutants
entering the house from outside air. The accu-
mulation of dust, dust mites, and tracked-in
soil in old carpets, sofas, and mattresses appears
to be a major source of exposure to lead, pesti-
cides, allergens, PAHs, and VOCs and can be
affected by cleaning habits such as the fre-
quency of vacuuming and the washing of bed
linen and towels (Roberts and Dickey 1995).
Other personal behaviors in indoor environ-
ments. Personal behaviors such as opening win-
dows and using exhaust fans can have significant
impacts on reducing exposures from activities
such as paint stripping (Riley et al. 2000).
Window-opening behaviors can have a strong
effect on a home’s air change rate; thus, this fac-
tor should be incorporated into exposure analy-
ses when estimating human exposure to indoor
air pollutants (Howard-Reed et al. 2002).
Behaviors related to heating and cooling the
building can also affect the air-exchange rate
and the prevalence of microbial and chemical
contaminants (Flannigan and Miller 2001).
Common household water-use activities such as
showering, clotheswashing, handwashing,
bathing, dishwashing, and indirect shower expo-
sure can increase indoor chemical exposures by
inhalation of vaporized or aerosolized chemicals
and by inadvertent ingestion of water. For
example, some of the greatest increases in sys-
temic exposure to trihalomethanes (THM) have
been associated with showering (direct and indi-
rect), bathing, and hand dishwashing (McKone
2005; Nuckols et al. 2005). Activities such as
cooking, arts and crafts, cleaning floors, and
painting can contribute to short-term increases
in indoor VOC levels. Diminished VOC levels
were achieved by turning on the air-condition-
ing system (Clobes et al. 1992). Activities shown
to generate considerable amounts of indoor par-
ticulate matter include cooking, smoking, clean-
ing, sources such as cigarette side-stream smoke,
pure wax candles, scented candles, a vacuum
cleaner, an air-freshener spray, a flat iron (with
or without steam) on a cotton sheet, electric
radiators, and electric and gas stoves (Afshari
et al. 2005).
A study by Ferro et al. (2004) of the per-
sonal, indoor, and outdoor particulate matter
(PM) concentrations for a variety of prescribed
human activities found that the activities that
resulted in the highest exposures to PM with
aerodynamic diameters ≥ 2.5 µm (PM2.5),
≥ 5 µm (PM5), and ≥ 10 µm (PM10) were
those such as dry dusting, folding clothes and
blankets, and making beds. Such activities dis-
turbed dust reservoirs on furniture and textiles.
The vigor of activity and type of flooring were
also important factors for dust resuspension.
The findings demonstrate that a wide variety of
indoor human resuspension activities increases
human exposure to PM and contributes to the
“personal cloud” effect (Ferro et al. 2004).
Consumer products and their use in resi-
dences. Various household products can be used
alone or together with other products for clean-
ing, cosmetics, or a variety of other purposes.
Consumer studies have found that there can be
large intra- as well as interindividual variation in
the frequency, duration, and amount of use of
products such as dishwashing detergents, pesti-
cides, cleaning products, and hair-styling prod-
ucts (Weegels and van Veen 2001). Common
household activities can raise exposures to
volatile organic chemicals (VOCs) up to a fac-
tor of 100 compared with exposures during the
sleep period and far above the highest observed
outdoor concentrations. Major associations of
consumer products with particular indoor
chemical exposures include deodorizers and the
level of p-dichlorobenzene, dishwasher and
laundry detergents and the level of chloroform,
smoking and the levels of benzene and styrene,
and painting and using paint remover and the
levels of n-decane and n-undecane (Wallace
et al. 1989).
Moreover, combinations of consumer
products, or a mix of consumer products with
outdoor air, can produce respiratory tract irri-
tants. Cleaning agents and air fresheners can
contain chemicals that react with other air cont-
aminants to yield potentially harmful secondary
products. For example, terpenes from consumer
products can react with ozone in indoor air to
generate secondary pollutants (Clausen et al.
2001; Nazaroff and Weschler 2004).
Home furnishings and decorating. Decisions
about home furnishings and decoration, such as
the types of furniture purchased, the presence of
carpets and curtains in various rooms, and
remodeling choices, can also affect indoor cont-
aminant exposures. For example, the remodel-
ing of a residence and the adoption of energy
conservation methods can reduce ventilation
and increase relative humidity. The changes in
these factors could increase the levels of dust,
dust mites, molds, VOCs, and other indoor air
pollutants (Roberts and Dickey 1995).
Household appliances. Decisions about the
types of appliances that are purchased can be
driven partly by personal cleaning habits, for
example, how clean the residence is kept.
Further, using air-conditioning while sleeping
can lead to a considerable build-up in the room
of carbon dioxide (CO2) from all types of air-
conditioning systems. These CO2 levels were
substantially higher than the levels in naturally
ventilated bedrooms. A survey was conducted to
investigate whether the occupants exhibited
Healthy building design
Environmental Health Perspectives • VOLUME 115 | NUMBER
6 | June 2007 967
Figure 2. U.S. government investments (US$) in
research to achieve healthy indoor environments
(Office of Management and Budget 1998).
Abbreviations: DOE, Department of Energy; EH, envi-
ronmental health; EPA, U.S. Environmental Protection
Agency; GSA, General Services Administration; NIH,
National Institutes Health; NSF, National Science
Foundation. Blue bars, total U.S. federal research
funding; black bars, U.S. built environment research
funding; GSA white bar, total construction dollars,
not total research dollars; NIH white bar, environ-
mental health research funding but not directly built
environment research funding.
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$11.6
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$0.58
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$0.04
symptoms of SBS while sleeping in air-condi-
tioned as well as naturally ventilated bedrooms.
Almost all occupants who used air-conditioning
while sleeping exhibited one or more SBS symp-
toms and usually displayed more SBS symptoms
after using air-conditioning than when they
used natural ventilation. The survey also
revealed that the frequency and duration of
using air-conditioning has an important impact
on the exhibition of the SBS symptoms (Wong
and Huang 2004).
Ongoing Developments in
Controlling Emissions from
Products and Building Materials
Today, more consumer products and building
materials are being studied and certified as low
chemical-emitting products and materials to
serve as primary control measures for achieving
good indoor air quality. Key products identified
by the U.S. Environmental Protection Agency
(EPA) as sources of indoor air pollution are
office furniture, flooring, paints and coatings,
adhesives and sealants, wall coverings, office
equipment, wood products, textiles, insulation,
and cleaning products. Product emission testing
protocols have been designed to help ensure
that the test results can be translated into real-
world product usage scenarios.
The American Society for Testing Materials
(ASTM) has established guidelines for measur-
ing chemical emissions using environmental
chambers. ASTM D5116-97 (ASTM 2007a)
and D6670-01 (ASTM 2007b) are the founda-
tion for some product-specific test protocols.
One testing laboratory, the Greenguard
Environmental Institute (GEI) in Atlanta,
Georgia, has established performance-based
standards to label goods with low chemical and
particle emissions for use indoors, primarily
building materials, interior furnishings, furni-
ture, cleaning and maintenance products, elec-
tronic equipment, and personal care products.
The standards of GEI establish certification
procedures, including test methods, allowable
emissions levels, product sample collection and
handling, testing type and frequency, and pro-
gram application processes and acceptance
(GEI 2005). The Carpet and Rug Institute’s
“Green Label” Testing Program for Carpets
and Vacuum Cleaners in Dalton, Georgia, is
another example of testing and certification of
low-emitting products (Carpet and Rug
Institute 2005).
“Smart” construction materials and coatings
are being developed through a test program for
innovative construction materials, with the goal
of decreasing indoor air pollution. One example
is the PICADA (Photo-catalytic Innovative
Coverings Applications for De-Pollution
Assessment) project, involving a European con-
sortium of private enterprises, research institu-
tions, and the European Commission’s Joint
Research Centre. The “smart” construction
materials (plaster, mortar, architectural concrete)
and coatings contain titanium dioxide (TiO2).
Nitrogen oxide (NOx) gases and organic com-
pounds diffuse through the porous surface of
the materials and coatings and stick to the TiO2
nanoparticles. Absorption of ultraviolet light by
the TiO2 leads to its photoactivation and the
subsequent degradation of the pollutants
adsorbed onto the particles. The acidic products
created by this process are washed away by rain
and/or neutralized by alkaline calcium carbonate
contained in the materials. Such new construc-
tion materials could help to reduce levels of
NOx gases that cause respiratory problems and
trigger smog production, and of other toxic sub-
stances such as benzene.
Tests with photocatalytic materials under
field conditions have shown that outdoor air
quality can be significantly improved. For
example, up to 60% reduction in the concen-
tration of NOx at street level was detected after
7,000 m2 of road surface in Milan, Italy, were
covered with a photocatalytic cementlike mate-
rial. Such new construction materials and coat-
ings could play a major role in helping meet the
European Union (EU) target of reducing NOx
levels to < 21 ppb/year by 2010. Although EU
researchers have focused on the development of
these types of materials for outdoor applica-
tions, future work is planned to determine
whether these products can also be used as
depolluting building materials and coatings in
indoor environments (PICADA 2005).
Fungal Resistance of
Construction Materials
and Finishes
Dampness, moisture, and mold problems in
buildings are a major factor affecting the quality
of indoor air worldwide [Institute of Medicine
(IOM) 2004]. These phenomena have a well-
documented link to health effects such as respi-
ratory symptoms and asthma (Bornehag et al.
2001, 2004; IOM 2004; Peat et al. 1998).
Various signs of dampness or moisture damage
are common in modern buildings (Nevalainen
et al. 1998), and the prevalence of observations
of mold varies from 1.5–20% (Bornehag et al.
2005; Anonymous 1993).
Dampness and mold are complex problems
both from the point of view of building con-
struction and human health. Although fungal
spores are present everywhere, it is when damp-
ness and moisture are uncontrolled that fungi
grow and thus develop into visible mold. Use of
fungicides or disinfection products do not solve
the problem and may even be an additional
load to indoor chemical exposures. Moisture
control may be difficult to manage in existing
buildings, and therefore any delay in the devel-
opment of actual mold damage allows time for
drying of the moistened materials. It is evident
that the materials of a healthy building should
be sturdy and resistant to microbial growth. It
is also evident that both dissemination of infor-
mation and access to training about the risks of
dampness and mold are necessary for control of
the problem. Training should be directed to
professionals in building design and construc-
tion as well as in building maintenance, man-
agement, and renovation. Furthermore, the
general public, as the users and occupants of
buildings, plays an important role in prevention
and control of these problems. Therefore, their
awareness of the risks of dampness and inter-
ventions to control it is critical.
Adan (1994) found that the finishing mate-
rials on buildings play a pivotal role in mold
growth and the quality of the indoor environ-
ment. Effects are most pronounced in places
with highly transient moisture loads such as
bathrooms. Regardless of insulation levels and
even with high ventilation rates, moistening of
surfaces cannot be avoided. Moisture retention
in the finish may cause sustained high surface
humidity, even when the indoor air is dry. This
explains why, in modern highly insulated
dwellings in cold and temperate maritime cli-
mates, mold risk is primarily a matter of mater-
ial properties. Considering the industrial trend
toward ecofriendlier products, which is gener-
ally accompanied by an increase in constituent
biodegradability, the situation is growing worse.
Therefore, a sustained strategy of indoor
fungal growth control must consider the piv-
otal role of finishing products. Two major
developments are promising:
• Research and development is under way in
the supply industry, with the goal of reduced
material susceptibility. This initiative is driven
primarily by environmental legislation and
concerns biocides in particular.
• Performance requirements in building codes
and/or consumer-oriented product labeling
are being considered for finishes. The finish-
ing materials very often are a designer’s or
consumer’s choice. Labeling can make the
end-user conscious of the consequences.
Reducing biosusceptibility. Presently, suffi-
cient resistance of materials to microbial attack
requires addition of biocides, with paints being
the main application area. There are two major
technical limitations in terms of release and
environmental impact.
First, the activity period of the biocide is usu-
ally much shorter (maximum 1–2 years) than the
desired service life of the finish, leading to early
replacement. Biocides tend to leach out quickly
in the early stages of the coating’s lifespan,
thereby decreasing the amount of active material
available for the longer term. Raising initial bio-
cide concentrations tries to counter this effect.
Biocides must be sufficiently mobile to find
their way to the surface. Consequently, biocides
are inherently sensitive to leaching, especially
when the surface is in direct contact with water.
To prolong the effective release period, a
viable approach is to incorporate a retarding step
Loftness et al.
968 VOLUME 115 | NUMBER 6 | June 2007 • Environmental
Health Perspectives
before the diffusion of the biocide to the surface
occurs. A number of such approaches have been
introduced. Most are based on reservoir proper-
ties of added porous materials such as zeolites
and silica (e.g., Edge et al. 2001). Other release-
concepts are emerging, addressing release-on-
demand (inclusion of nanopackages), slow
release, and so-called bioswitches, which have
been applied successfully in other areas such as
medical applications and food packaging.
Second, most traditional biocides, for
example, mercury compounds, are or will soon
be under prohibitive rules. In this context, the
EU Biocides Directive 98/8/EC (European
Parliament and the Council of the EU 1998)
reflects a tightened environmental policy.
Therefore, European industries are eagerly
searching for ecofriendlier alternatives.
Toward performance requirements and
product labeling. The recognition of the crucial
role of the interior finish calls for an approved
method for assessing the its mold control per-
formance. Such a method is a basic instrument
for product labeling and end-user implementa-
tion. In addition, control of fungal growth on
materials has been identified as a priority in EU
member states responding to mandate M/366
(approved November 2004; EU Commission
2005c). The CPD applies to all construction
products that are produced for or incorporated
within building and civil engineering construc-
tion works. It harmonizes all construction
products subject to regulatory controls for
marking purposes.
Present methods use a single moisture
regime and do not explicitly consider effects of
transient moisture loads and subsequent mater-
ial performance in relation to the transient loads.
Most tests are based either on a more or less
steady-state level of the relative humidity below
saturation (Anonymous 1968, 1975, 1978,
1986, 1988a) or unambiguous surface moisten-
ing (Anonymous 1988b, 1989a, 1989b). Adan
et al. (1999) proposed a new test that considers
the effect of indoor climate dynamics.
Pilot application of the test during the past
decade yielded a highly reproducible and dis-
criminating picture of material performance in
terms of fungal resistance and showed perfor-
mance that might differ considerably based on
the moisture load. Tests were conducted specifi-
cally on silicon caulking typically applied in san-
itary rooms (Adan and Lurkin 1997a); a wide
range of coating types including waterborne
interior paints (Adan et al. 1999); specialties
such as high-absorbing claddings (Adan and
Lurkin 1997b) and ceramic coatings (Sanders
2002a); fiber products, gypsum-based plasters,
and wallpapers including glues (Adan et al.
1999); and cement-based panels (Sanders
2002b). Fungal resistance was found to be a
product-based feature and application oriented,
emphasizing the importance of indoor climate
dynamics for mold resistance. These findings
laid the foundation for an approved product
qualification system in the Netherlands with
respect to fungal resistance. Such a system is a
step toward performance requirements in build-
ing regulations. Moreover, product labeling pro-
vides support to end users, i.e., tenants and
building owners, the actual occupants.
Labeling is defined by a three-level classifi-
cation system: I, resistant; II, fairly resistant;
and III, sensitive (Table 1). These definitions
are based on analysis of the entire growth pat-
tern as a function of time (Adan 1995; Adan
et al. 1999).
The basic principle underlying the classifi-
cation system is the potential of most products
to exhibit widely divergent behavior as a func-
tion of the moisture load. In the past decade, in
about 50% of the tested products, steady-state
and transient (i.e., condensation) conditions
showed highly differing behavior, underlining
the importance of considering both climatic
conditions in assessing product performance.
Consequently, a labeling system should be con-
nected to a recommended application. The best
quality (labeled “I”) in terms of resistance
reflects that the majority of mold problems
occurs in indoor areas with a distinct vapor pro-
duction [e.g., bathrooms and kitchens in 60
and 40% of cases in the Netherlands, respec-
tively (Anonymous 1993)]. In all other indoor
areas, with a more or less steady-state indoor
humidity, risks of surface growth are a conse-
quence of interaction of finishing product,
building construction—thermal bridging in
particular—and average humidity or ventila-
tion. In these cases, product labeling discrimi-
nates between fairly resistant products that can
be applied on thermal bridges and sensitive
products that should be applied only on inner
constructions in dry environments.
Conclusions
We discussed the issue of how to design a
healthy building from three viewpoints. The
first approach describes sustainable develop-
ment, focusing on what should be considered
in design and land use. Second, the analysis of
how occupants affect their indoor air quality
links the everyday use of the building to its
design. Third, the overview of recent develop-
ments in products and materials and their cer-
tification and labeling indicates a trend toward
addressing current problems.
Sustainable design rediscovers the social,
environmental and technical values of pedes-
trian, mixed-use communities, using existing
infrastructures, including main streets and
small-town planning principles, and recaptur-
ing indoor–outdoor relationships. Sustainable
design introduces benign, nonpolluting materi-
als and assemblies with lower energy require-
ments and higher durability and recyclability.
Humans have a major role in maintaining
the healthy indoor environment, especially in
residences. This role includes personal cleaning
habits and other personal behaviors. The occu-
pants of the building decide the types of con-
sumer products to be used and furnishings and
appliances to be purchased, as well as where
and how they are used. Thus, the occupant has
a key role in determining the quality of indoor
air in his/her residence.
Certification of consumer products and
building materials as low-emitting products is a
primary control measure for achieving good
indoor air quality. Key products in this respect
are office furniture, flooring, paints and coat-
ings, adhesives and sealants, wall coverings,
wood products, textiles, insulation, and clean-
ing products. The finishing materials have a key
role in moisture retention and mold growth.
The goal of product development is to reduce
material susceptibility, to establish performance
requirements for finishes in building codes and
to require consumer-oriented product labeling.
Training professionals in various fields of
design, construction, maintenance, and man-
agement of the building is necessary in devel-
oping healthier environments for living and
work. Dissemination of information concern-
ing the healthiness of the indoor environment
and what a consumer can do about it is essen-
tial to increase root-level activities toward
obtaining and maintaining healthier buildings.
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Table 1. The Dutch classification system for fungal resistance
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Washington, DC:U.S. Department of Labor.
U.S. DOL. 2003b. Job Openings and Labor Turnover Survey.
Washington, DC:U.S. Department of Labor.
U.S. DOL. 2004a. National Compensation Survey: Occupational
Wages in the US, July 2003. Washington, DC:U.S. Depart-
ment of Labor.
U.S. DOL. 2004b. Employer Cost for Employer Compensation,
June
2004, USDL 04-1805. Washington, DC:U.S. Department of
Labor.
U.S. EPA. 1998. Cost of Illness Handbook 1991–1996.
Washington,
DC:U.S. Environmental Protection Agency.
Wallace LA, Pellizzari ED, Hartwell TD, Davis V, Michael LC,
Whitmore RW. 1989. The influence of personal activities
on exposure to volatile organic compounds. Environ Res
50:37–55.
Weegels MF, van Veen MP. 2001. Variation of consumer
contact
with household products: a preliminary investigation. Risk
Anal 21:499–511.
Wong NH, Huang B. 2004. Comparative study of the indoor air
quality of naturally ventilated and air-conditioned bed-
rooms of residential buildings in Singapore. Build Environ
39:1115–1123.
Wyon DP. 1996. Indoor Environmental Effects on Productivity.
In:
Proceedings of IAQ96. Paths to Better Building Environments,
Baltimore, MD. Atlanta:American Society of Heating
Refrigerating and Air-Conditioning Engineers, Inc., 5–15.
Real Estate Principles
A Value Approach
Fifth Edition
Chapter 4
Government Controls and Real Estate Markets
© McGraw-Hill Education. All rights reserved. Authorized only
for instructor use in the classroom. No reproduction or further
distribution permitted without the prior written consent of
McGraw-Hill Education.
Limits on OwnershipRestrictions of UseSeparation of Use or
PossessionComplete RemovalShare of ValuePrivateDeed
Restrictions/ HOA or Condo BylawsEasements & LeasesLiens
(In default)________GovernmentRegulation through Police
Power_______Eminent DomainTaxation
This chapter examines the government limitations on real
property ownership
© McGraw-Hill Education.
4-‹#›
Land use is one of the most regulated activities in our society.
Why?
Must it be this way?
© McGraw-Hill Education.
4-‹#›
Features of Real Estate that Cause Market Distortions
“Spillover” effects from nearby land uses
Uniqueness of location (absolute monopoly)
Unknown quality or condition of existing structures
Instability of land uses around residential neighborhoods
© McGraw-Hill Education.
4-‹#›
Resulting Market Failures in Real Estate (1 of 2)
Monopoly
Utilities as “natural” monopolies
“Holdouts” in land assembly efforts (roads, other public uses)
Incomplete information
Construction quality hidden
Buyers unable to judge natural risks
Hurricanes
Earthquakes
Fires
© McGraw-Hill Education.
4-‹#›
Resulting Market Failures in Real Estate (2 of 2)
Buyers unable to judge adequacy of structure quality
Wind tolerance
Resilience against shocks
Fire safety and resistance
© McGraw-Hill Education.
4-‹#›
More Market Failures (1 of 2)
Externalities
“Spillover” effects of land use for which initiator is not held
accountable
Traffic congestion
Storm runoff
Emissions (smoke, gases, particles, noise, light)
Urban sprawl
Disorderly extension of urban infrastructure
© McGraw-Hill Education.
4-‹#›
More Market Failures (2 of 2)
Uncertainty of residential values
Effect of non-conventional structures
Effect of nonresidential land uses
Effect of non-conventional population –e.g., students
© McGraw-Hill Education.
4-‹#›
The “Revolution” in Land Use Controls
Pre-1970: Little interest in land use controls
No land use plans had force of law
Zoning very limited in function
Focused on protection of single-family homes
Did not exist in many areas
Environmental movement of late 1960s
Rachael Carson: Silent Spring
Love Canal
Notion of “spaceship earth”
© McGraw-Hill Education.
4-‹#›
Some Critical Questions
Will land use planning solve market failures?
At what level should control be imposed?
For subdivisions?
For streets and utilities?
For schools?
For water resources and drainage control?
For transportation systems?
For rivers and wetlands?
For ecological and endangered species?
© McGraw-Hill Education.
4-‹#›
Is Comprehensive Planning the Answer? What Is Required?
Project future population growth
Determine requirements for water and waste disposal
Project needs for public services (utilities, streets, schools,
parks and recreation, safety)
Projected demand for various land uses (public, residential,
nonresidential)
Design compatible arrangement of needed land uses (land use
map)
© McGraw-Hill Education.
4-‹#›
Challenges to Comprehensive Planning
Changing notion of “best practice”
Cul-de-sacs or grid streets?
Mixed density and mixed use or containment of nonresidential
use?
How much mass transit?
Limited actual experience to rely on (little more than 30 years)
Insufficient theory and information
Inability to foresee the future well
© McGraw-Hill Education.
4-‹#›
Traditional Planning versus New Urban Planning (1 of 2)
Traditional
Separated uses
Automobile oriented
Priority placed on easy ingress and egress
Uniform density
Cul-de-sac hierarchy in neighborhoods
© McGraw-Hill Education.
4-‹#›
Traditional Planning versus New Urban Planning (2 of 2)
New Urban
Mixed use
Public transportation
Pedestrian oriented
Sidewalks
Houses close to street
Rear alleys
Grid streets with restricted traffic flows
© McGraw-Hill Education.
4-‹#›
Traditional Land Use Controls: Building Codes
Older than zoning (circa 1900)
Issues of safety
Fire: Materials, alarms, electrical and gas systems
Sanitation: Plumbing, water, and HVAC requirements
Injury: Design and strength
Continue to evolve
Effect of Hurricane Andrew, 2004-5 hurricanes, Katrina
New technology (e.g., smoke detectors)
Changing perception of needs (e.g., bedroom windows large
enough to step through)
© McGraw-Hill Education.
4-‹#›
Traditional Land Use Controls: Zoning
Features of traditional zoning
Use classifications: Residential, commercial, industrial,
automotive
Use districts (zoning map)
Setback requirements (side, front and back)
“Bulk” or density limits (minimum lot size, height limits,
maximum floor area ratios)
Special use districts: Service stations, hospitals, churches,
private schools, cemeteries
© McGraw-Hill Education.
4-‹#›
Traditional Land Use Controls: Subdivision Regulations
Features of subdivision regulations
Standards for streets, sewers, and water systems
Adequate water supply for fire safety
Adequate drainage and run-off retention
Open spaces
Lot layout
Easements for utilities
Traffic and pedestrian safety
© McGraw-Hill Education.
4-‹#›
Traditional Land Use Controls: Planning and Zoning
Administration (1 of 2)
Planning and Zoning Commission created in the zoning
ordinance
Appointed by elected officials
Ultimately is advisory to elected officials
Oversees implementation of the ordinance
Considers requests for specific changes
Requested changes must:
© McGraw-Hill Education.
4-‹#›
Traditional Land Use Controls: Planning and Zoning
Administration (2 of 2)
Be compatible with a comprehensive plan
Be justified if they require change in the comprehensive plan
Not have undue effect on surrounding land uses or the
community
© McGraw-Hill Education.
4-‹#›
Traditional Land Use Controls: Board of Adjustment
Required in zoning ordinance
Appointed by elected officials
Reviews petitions for variances
Decisions are final rather than advisory to the elected officials
Only appeal is through the courts
© McGraw-Hill Education.
4-‹#›
Traditional Land Use Controls: Site Plan Review
May be the same as planning and zoning commission
Review subdivisions and most other building site plans
Public review (neighbors and others)
Public offices (public safety - fire, police, emergency vehicles;
utility officials; school officials)
Informal procedure allows criteria and rules to change with
public pressure
Most “treacherous” step for proposed new development?
© McGraw-Hill Education.
4-‹#›
Zoning Issues and Concepts (1 of 2)
Legality of zoning established by USSC: Village of Euclid
versus Ambler Realty - 1926
Nonconforming use: Use conflicting with zoning map, but
existing prior to its enactment
Cannot be substantially changed
Must be continuous
Can be “amortized” away (e.g., billboards)
© McGraw-Hill Education.
4-‹#›
Zoning Issues and Concepts (2 of 2)
Variance: Exception to requirements granted due to hardship
Common example: wavier of setback requirement
Exclusionary zoning (unreasonable lot size; inadequate
provision for low- and moderate-income housing)
© McGraw-Hill Education.
4-‹#›
Do Land Use Controls Solve the Problem of Market Failure?
Does zoning raise the cost of “threshold” housing
unnecessarily?
Does it interfere with economically efficient land use patterns?
Example: Does zoning make neighborhood services excessively
remote?
Does low density resulting from zoning contribute to urban
sprawl?
Houston: effective land uses without zoning?
© McGraw-Hill Education.
4-‹#›
Newer Approaches to Land Use Control: Planned Unit
Development
Detailed development plan negotiated with authorities
Mixed use
Mixed density
No standard setback requirements
Open community spaces
Community recreation and other facilities
© McGraw-Hill Education.
4-‹#›
Newer Approaches to Land Use Controls: Performance
Standards
Storm runoff limits
Noise and emission limits
Traffic impact limits
Tree removal restrictions
© McGraw-Hill Education.
4-‹#›
More New Land Use Controls
Impact fees
Favorite of economists (in principle)
Despised by many in the building community
Appear to be used more as revenue source than tool to guide
land use
Growth restrictions
Temporary moratoriums
US Supreme Court refuses to review Petaluma, Ca. limit on the
number of new housing units.
Also Boulder, Co., and Boca Raton, Fl.
© McGraw-Hill Education.
4-‹#›
Another Way? Form Based Zoning
Land uses are determined not by prescription but “organically”
based on:
Development density
Street character
Parking arrangements
Walkway character
Structure shapes and sizes
Foliage character
© McGraw-Hill Education.
4-‹#›
How Form-Based Zoning Works (1 of 2)
Within broad categories, land uses can go anywhere
Households will select a form that suites their location,
household and lifestyle preference: rural, suburb, urban core
Non-residential uses will select as their business requires:
© McGraw-Hill Education.
4-‹#›
How Form Based Zoning Works (2 of 2)
Neighborhood shops versus large urban stores
Small local offices versus financial centers
Example: Denver, Colorado
http://formbasedcodes.org/codes/denver-commons/
© McGraw-Hill Education.
4-‹#›
Spaceship Earth?
What are other effects of the “spaceship earth” scenario?
© McGraw-Hill Education.
4-‹#›
Sample of Environmental Controls since the Late 1960s
Clean Air Act
Clean Water Act
Comprehensive Environmental Response Compensation and
Liability Act (CERCLA)
Occupational Safety and Health Act (OSHA)
Endangered Species Act
Increasing limitations on “fracking”
© McGraw-Hill Education.
4-‹#›
Some Hazardous Materials
Asbestos and fiberglass
PCBs
Leaking underground storage tanks (LUSTs)
Radon
Mold
© McGraw-Hill Education.
4-‹#›
Is there a limit to regulation?
Pennsylvania Coal Company v Mahon (US Supreme Court,
1922):
Courts must balance public safety and welfare against taking of
property
At some point eminent domain must be used. (Murr v.
Wisconsin now before USSC)
Minority opinion in the case: “We are in danger of forgetting
that a strong public desire to improve the public condition is not
enough to warrant achieving the desire by a shorter cut than the
constitutional way of paying for it.”
© McGraw-Hill Education.
4-‹#›
Power of Eminent Domain
Eminent domain: Right of government to acquire private land,
without the owner’s consent, for public use, with due process
and just compensation
Condemnation: Legal procedure for exercising the right of
eminent domain
Public use versus public purpose
Just compensation based on highest and best use
Problems of excessive use
Inverse condemnation
© McGraw-Hill Education.
4-‹#›
Eminent Domain Controversy - I
Concept of “public use” expanded to “public purpose”
US Supreme Court in 1954 allowed condemnation of “blighted
areas” for private redevelopment
Michigan Supreme Court in 1981 allowed condemnation to
enable GM manufacturing facilities
Wide-spread subsequent condemnation of “blighted areas” for
private redevelopment
Driven by local government hunger for an increased property
tax base
© McGraw-Hill Education.
4-‹#›
Eminent Domain Controversy – II
Kelo v. New London Ct., 2005
U.S. Supreme Court allowed use of eminent domain to obtain
non-blighted property for private redevelopment
Left it to states to decide whether to intervene
Most states initiated legislation to limit use of eminent domain
Congress enacted law to prevent application of Federal monies
for such use
Most states moderated the proposed laws to limit eminent
domain
http://www.youtube.com/watch?v=4N1svadJQ40
© McGraw-Hill Education.
4-‹#›
A Larger Perspective on “Kelo” (1 of 2)
New London, Ct., had been long recognized as an abandoned
and depressed community.
A community/state plan of redevelopment had evolved, with
subsidies from the state.
Achievement of the plan required removal of all of the houses
in the Kelo area.
© McGraw-Hill Education.
4-‹#›
A Larger Perspective on “Kelo” (2 of 2)
“Kelo” can hardly be viewed as an isolated or arbitrary taking.
Greatest significance of the USSC “Kelo” decision?- Shift of
authority back to the states.
© McGraw-Hill Education.
4-‹#›
The Effect of Property Taxes on Real Estate
Can property taxes reduce property values and property wealth?
Can an efficient property tax enhance property values and
property wealth by the services it funds?
© McGraw-Hill Education.
4-‹#›
Property Taxes
A primary source of local government revenue
Reliable and countercyclical
Many taxing authorities
City
Improvement districts
County
Transportation authorities
Schools
Water management districts
© McGraw-Hill Education.
4-‹#›
Property Exempt from Taxes
Religious organizations
State Property
Nonprofit organizations
Homestead
Educational institutions
© McGraw-Hill Education.
4-‹#›
Determination of Tax Rate
© McGraw-Hill Education.
4-‹#›
Computing Tax LiabilityMarket value$150,000Assessed
value135,000 = (0.90 × MV)Less: exemptions25,000Taxable
value$110,000
Property Tax CalculationTaxing AuthorityMillage RateTaxes
LeviedCounty8.58$ 943.80City3.20352.00School
district9.861,084.60Water mgt.
district0.055.50Total21.692,385.90
© McGraw-Hill Education.
4-‹#›
Special Assessments
Special assessments: Taxes for specific public improvements
affecting a property
Street, sewer, etc.
Usually charged on a per front foot basis
Example: Street improvements of $500 per running foot of
street
For lot with 100 feet of frontage:
100 × .5 × $500 = $25,000
© McGraw-Hill Education.
4-‹#›
Special Assessments and Community Development Districts
Many large subdivisions have private community development
districts
Create and maintain neighborhood infrastructure
Utilities
Drainage and water retention
Streets, bikeways, walkways
Recreation facilities
Issue tax-exempt bonds and impose property assessments to pay
the obligations
Have the same lien priority as property taxes
© McGraw-Hill Education.
4-‹#›
An Example CDD Community in Florida: The Villages
Retirement community in north-central FL
10 CDDs provide every community service except criminal law
enforcement
Population of over 100,000
http://www.thevillages.com/AboutUs/aboutus.htm
© McGraw-Hill Education.
4-‹#›
Issues with Property Tax
Regressive?
May be regressive viewed alone
Not necessarily regressive if resulting public services also are
considered
Uneven across geographic areas and property types
Distorted by differential protection laws
California – Proposition 13
Florida – “Save our Homes” Amendment
Poorly administered
© McGraw-Hill Education.
4-‹#›
Summing up (1 of 2)
Land use must be regulated due to market failures
The concept of spaceship earth has brought a revolution in land
use controls
Traditional controls: building codes, zoning, subdivision
regulations
“Post-revolution” controls: impact fees, performance standards,
PUDs, environmental laws
© McGraw-Hill Education.
4-‹#›
Summing up (2 of 2)
When regulation goes too far: eminent domain
The problem of expanding use
Property taxes as a double-edged sword.
Efficient and reliable tax.
Can be inequitable and distort land use
© McGraw-Hill Education.
4-‹#›
End of Presentation
© McGraw-Hill Education. All rights reserved. Authorized only
for instructor use in the classroom. No reproduction or further
distribution permitted without the prior written consent of
McGraw-Hill Education.
4-‹#›
(
)
(
)
(
)
(
)
20mills
or
percent.
2
of
rate
tax
a
or,
.020
0
500,000,00
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2,500,000,
25,000,000
65,000,000
or
exemptions
property
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assessed
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source
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2/18/2020 Sample Content Topic
https://purdueglobal.brightspace.com/d2l/le/content/115680/vie
wContent/9224752/View 1/2
Technology and Indoor Environments
You read briefly about hazardous materials and gasses, and
practiced with environmental vocabulary concerning
property sales in the Learning Activity. Now you have an
opportunity to do some research and see what technological
advances have helped to either eradicate or mitigate the
damages done by environmental toxins with regards to real
property. Most states have laws pertaining to responsibility
for disclosure of such toxins present in homes.
The following Course Outcome is assessed in this
assignment:
GEL-3.04: Examine the relationship between science and
technology and the impact on the natural world.
Scenario: You are showing clients a house built in 1960 in
your state. They are interested in buying the home, but they
want to completely remodel it and the mechanical systems
including adding a new gas furnace and stove. Research
"Healthy Building Materials" in the Purdue Global Library
located in the Academic Tools area of the course. Select an
article to read and record the title, author, and year.
Checklist:
What air quality and building materials concerns should
they look at regarding the existing home? Analyze possible
radon, lead, gas, and asbestos issues and how these
affect homeowners and the environment.
What scientific discoveries regarding air quality and
building materials have led to new technological solutions
that will deal with your clients’ potential problems?
Based on research on your state’s disclosure statements
required of real estate agents, discuss what disclosures of
Assignment Details
2/18/2020 Sample Content Topic
https://purdueglobal.brightspace.com/d2l/le/content/115680/vie
wContent/9224752/View 2/2
hazardous materials the real estate agent or seller is
required to make to the buyer of a home in your state.
Access the Unit 3 Assignment grading rubric.
Respond in a minimum 500–600-word APA formatted and
citation styled paper with additional title and reference
pages to the Unit 3 Assignment Dropbox before the end of
the unit.
https://kapextmediassl-
a.akamaihd.net/business/MT361/1904c/rubrics/u3_rubric.pdf
https://kapextmediassl-
a.akamaihd.net/business/MT361/1904c/apa_format_style.pdf

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  • 1. Jennifer’s Post I had a difficulty finding non-reactive studies for the particular research that I have been focusing on. The first one that I found seems to be both reactive and non-reactive. People were involved in the first portion of the study, but were not aware of the second phase. The first academic journal that I found is titled “Does Counting Emotion Words on Online Social Networks Provide a Window into People’s Subjective Experience of Emotion? A Case Study on Facebook. Content analysis was used to determine if the words that people post are linked to how they really feel. Reactive measures were used first to question participants on how they felt during the week. Word counting algorithms were used to determine if people really feel the way that they portray on social media. Four samples were used for the study. Facebook data and experience surveys were used to determine if emotion words can be linked to somebody’s true emotional status. The multi-level data analysis included four phases. It was found that there is not a link between a person’s emotions and the words that they post on social media. (Kross, et al., 2019) The second article that I found is titled “Objectifying Fitness: A Content and Thematic Analysis of #Fitspiration Images on Social Media. Non -reactive measures were used to determine if the large volume of #fitspiration posts on Instagram are linked to body dissatisfaction. Hashtags such as #fitspiration were analyzed in terms of body types and how the posts were presented. The purpose is to find the link between the images and the theory of objectification. It theorizes the dangers of women being bombarded by what is considered an ideal body type. The first question that was asked was "What are the most common types of imagery featured in #fitspiration posts on Instagram?” (Deighton, Bell, 2018). The posts were coded into categories such as body type, body proportion, pose and clothing type. It was found that the majority of the posts depict
  • 2. thin people with low body fat. In a second study that used content analysis the themes of #fitspiration was looked at. In both studies objectification theory was seen. In both studies, thinness is linked to beauty in unrealistic ways that can be detrimental to peoples body image. For me, finding non-reactive studies were difficult. Many of the articles that I found included surveys as the primary measure, or both reactive and non- reactive measures. This makes me think that it could be difficult to gain physical evidence regarding social media usage without violating privacy or other ethical concerns. References Deighton-Smith, N., & Bell, B. T. (2018). Objectifying fitness: A content and thematic analysis of #fitspiration images on social media. Psychology of Popular Media Culture, 7(4), 467– 483. https://doi.org/10.1037/ppm0000143 Kross, E., Verduyn, P., Boyer, M., Drake, B., Gainsburg, I., Vickers, B., Ybarra, O., & Jonides, J. (2019). Does counting emotion words on online social networks provide a window into people’s subjective experience of emotion? A case study on Facebook. Emotion, 19(1), 97–107. https://doi.org/10.1037/emo0000416.supp (Supplemental) Paul’s Post Articles: McKibben, W. B., Umstead, L. K. & Borders, L. D. (2017). Identifying dynamics of counseling Leadership: A content analysis study. Journal of Counseling & Development, 95(2), 192–202. https://doi.org/10.1002/jcad.12131 Burbank, M., Odom, S. F., & Sandlin, M.R. (2015). A content analysis of undergraduate students’ perceived reasons for changes in personal leadership behaviors. Journal of Leadership Education, 14(2), 182–197. https://doi.org/10.12806/V14/I2/R12 Textbook: Neuman, W. L. (2017). Understanding research. New York, NY:
  • 3. Pearson. Topics: The first article chosen discusses the relationship between leadership and counseling. The study wanted to seek "how counseling leadership works as a social dynamic by identifying the content and processes involved" (McKibben et al., 2017). Many components across leaderships theories emerged such as positive reinforcement and mentorship. The second article reviewed seeks to help change leadership for undergraduates after they have taken a course in leadership practices. "Individuals learn and develop leadership through a variety of mediums such as formal coursework, youth and collegiate programs, educational experiences, and on-the-job experiences" (Brungardt, 1997; Cress, Astin, Zimmerman-Oster, & Burkhardt, 2001; Dugan, 2006). "Understanding the link between leadership development and leadership education is essential as leadership educators attempt to expand the capacities of individual students in the classroom through curricular activities and outside the classroom through co- curricular assignments" Article findings: Article one: "On the basis of a systematic coding procedure, we identified 24 themes that described leadership dynamics in the counseling profession (Research Question 1), which were then grouped by commonalities into three broad categories (Research Question 2)" (McKibben et al., 2017). The researchers used content analysis by using "an inductive coding approach to allow themes to emerge without the constraints of an a prior theory" (Krippendorff, 2013). Full length articles were used from counseling journals. An inductive approach was used in order for them to randomly select two articles as a pretest.
  • 4. Article two: The article wanted readers to know that a Student-Leadership Practices Inventory was conducted. This was a pre/post assessment. Students must be enrolled in a leadership course, needed to complete the student inventory, and respond to reflection prompts. The class used the Kolb's Experimental Learning Model to reflect on their changes in leadership qualities. This study used content analysis which is a "nonreactive technique that lets you examine both hidden and visible content in communication messages" (Neuman, p. 163, 2017). Specifically, the researchers used the instructors for the course. In order to prevent potential bias in results, "the analysis of the student reflections and consent to participate in the study was not conducted until the conclusion of the course. As another way to limit bias, names were removed and reflections were coded by someone other than the instructor before analysis was conducted" (Burbank, M., Odom, S. F., & Sandlin, M.R. (2015). Made you think: The articles that I chose made me reflect in a few ways with regards to nonreactive measures. First, finding articles that relate to your topic is important. Narrowing down what it is specifically want you want to research is key to maintain direction. To help guide in a content analysis there is an eight step process. To name two portions in our steps would be identify text to analyze and decide on units of analysis. A coding system using leadership theory would be sufficient for my research proposal. "You must tailor the coding system to the specific type of text or communication medium you are examining, such as television dramas, novels, music videos, photos in magazine advertisements, and so forth" (Neuman, p. 164, 2017). Then I must break down to the unit of analysis, such phrases for leaderships would be "coaching," leaderships" and "mentor".
  • 5. A healthy building is based on the successful fulfillment of many requirements. For each building, sound design and construction are necessary for its technical functioning and mechanical stability and for the basic safety of its occupants. However, this is not sufficient to ensure indoor environmental quality (IEQ) for its occupants. There are a number of other fac- tors that affect the occupants’ well-being either directly or indirectly. Among such factors are heating, ventilation and air conditioning, and activities of the occupants, including the use of office equipment or household activities such as cooking, cleaning, or applying pesticides. The risk assessment of indoor contaminants and the effectiveness of interventions are chal- lenges faced globally because of vast differences in the types of residences and their climates as well as the many types of household products, furniture, appliances, and so on, that are avail- able to consumers today. Examples of these diverse challenges have been demonstrated in the book The Material World that provides detailed, thought-provoking visual and written portraits of “statistically average” families and their households in 30 nations around the world (Menzel 1994). Indoor air pollution is not a new problem, although only recently has it become a matter of public concern. As early as the 18th century, hygienists had identified the consequences of
  • 6. inadequate ventilation in the indoor environ- ment. Systematic research activities emerged soon after World War II, in some respects reversed by energy conservation measures intro- duced in housings after the oil crisis in the early 1970s. Since then, the complexity and the health relevance of the indoor environmental problem have become increasingly apparent (European Commission 2005a, 2005b). Failures to control indoor air risks have huge economic consequences in the form of health care costs, lost working days, and per- sonal costs to individuals (Mendell et al. 2002). Consequently, investments in developments that pursue enhanced human health and well- being through healthier indoor environments should not be seen as business nuisances but should be weighed against the benefits gained. Because factors contributing to building health are complex, with connections to many essential fields, we do not attempt to cover all aspects but present three essential ideas: sustainable develop- ment of buildings and communities, the effect of occupants on the indoor environment, and recent developments in creating healthier prod- ucts and building materials with a focus on moisture and mold control. These three areas are important because they address the most current issues in building design: sustainability (in terms both of natural resources and of the lifetime of the building); individual behaviors and how they affect their indoor environments; and the newest trends in building materials that
  • 7. can promote healthier indoor environments. Environmental Sustainability Contributes to Health, Productivity, and Quality of Life Sustainable design is a collective process whereby the built environment achieves eco- logic balance in new and retrofit construction toward the long-term viability and humaniza- tion of architecture. In an environmental con- text, this process merges the natural, minimum resource-conditioning solutions of the past (daylight, solar heat, natural ventilation) with the innovative technologies of the present into an integrated “intelligent” system that supports individual control to achieve environmental quality with resource consciousness. Sustainable design rediscovers the social, environmental, and technical values of pedestrian, mixed-use communities, fully using existing infrastruc- tures, including “main streets” and small-town planning principles and recapturing indoor– outdoor relationships. It attempts to avoid the thinning out of land use and the dislocated placement of buildings and functions caused by single-use zoning. Sustainable design introduces benign, nonpolluting materials having lower operating energy requirements and higher durability and recyclability. Finally, sustainable design offers architecture of long-term value through modifiable building systems through life-cycle instead of least-cost investments and through timeless delight and craftsmanship (Loftness et al. 2005). The importance of proving that sustain-
  • 8. able design and engineering improves health, productivity, and quality of life has never been more important. To this end, the Center for Building Performance at Carnegie Mellon University in collaboration with the Advanced Building Systems Integration Consortium (ABSIC) from 2000 to the pre- sent have been developing a building invest- ment decision support tool—BIDS (Carnegie Mellon, Pittsburgh, PA). This cost–benefit tool presents the life-cycle data of over Environmental Health Perspectives • VOLUME 115 | NUMBER 6 | June 2007 965 Research | Mini-Monograph This article is part of the mini-monograph “Developing Policies to Improve Indoor Environmental Quality.” Address correspondence to A. Nevalainen, Neulanie- mentie 4, FI-70700 Kuopio, Finland. Telephone: 358 17 201 342. Mobile: 358 400 587 634. Fax: 358 17 201 155 E-mail: [email protected] The authors declare they have no competing financial interests. Received 9 January 2006; accepted 25 January 2007. Elements That Contribute to Healthy Building Design Vivian Loftness,1 Bert Hakkinen,2 Olaf Adan,3 and Aino Nevalainen 4 1Carnegie Mellon University, School of Architecture, Pittsburgh, Pennsylvania, USA; 2Gradient Corporation,
  • 9. Cambridge, Massachusetts, USA; 3TNO Built Environment and Geosciences, Delft, the Netherlands; 4National Public Health Institute, Department of Environmental Health, Kuopio, Finland BACKGROUND: The elements that contribute to a healthy building are multifactorial and can be discussed from different perspectives. OBJECTIVES: We present three viewpoints of designing a healthy building: the importance of sus- tainable development, the role of occupants for ensuring indoor air quality, and ongoing develop- ments related to indoor finishes with low chemical emissions and good fungal resistance. DISCUSSION: Sustainable design rediscovers the social, environmental, and technical values of pedestrian and mixed-use communities, using existing infrastructures including “main streets” and small-town planning principles and recapturing indoor–outdoor relationships. This type of design introduces nonpolluting materials and assemblies with lower energy requirements and higher dura- bility and recyclability. Building occupants play a major role in maintaining healthy indoor envi- ronments, especially in residences. Contributors to indoor air quality include cleaning habits and other behaviors; consumer products, furnishings, and appliances purchases, as well as where and how the occupants use them. Certification of consumer products and building materials as low- emitting products is a primary control measure for achieving good indoor air quality. Key products in this respect are office furniture, flooring, paints and coatings,
  • 10. adhesives and sealants, wall cover- ings, wood products, textiles, insulation, and cleaning products. Finishing materials play a major role in the quality of indoor air as related to moisture retention and mold growth. CONCLUSIONS: Sustainable design emphasizes the needs of infrastructure, lower energy consump- tion, durability, and recyclability. To ensure good indoor air quality, the product development for household use should aim to reduce material susceptibility to contaminants such as mold and should adopt consumer-oriented product labeling. KEY WORDS: consumer products, dampness, emissions, fungal resistance, healthy buildings, indoor air, sustainable development, ventilation. Environ Health Perspect 115:965–970 (2007). doi:10.1289/ehp.8988 available via http://dx.doi.org/ [Online 25 January 2007] 200 case studies—laboratory, field, and simu- lation studies that reveal the substantial envi- ronmental benefits of a range of advanced and innovative building systems. The health bene- fits of high-performance buildings designed to deliver high-quality air, thermal control, light, ergonomics, privacy, and interaction as well as access to the natural environment were ana- lyzed (Center for Building Performance and Diagnostics/Advanced Building Systems Integration Consortium 2005). The following components were included: • healthy, sustainable air;
  • 11. • healthy, sustainable thermal control; • healthy, sustainable light; • workplace ergonomics and environmental quality; • access to the natural environment; and • land use and transportation. Healthy, sustainable air. This component depends on commitments to improve the qual- ity and quantity of outside air, maximize nat- ural ventilation with mixed-mode heating, ventilating, and air-conditioning (HVAC) sys- tems, and separate ventilation air from thermal conditioning, provide task air and individual control, and improve pollution source control and filtration. International case studies have demonstrated that high-performance ventila- tion strategies reduce respiratory illness 9–20% and increase individual productivity between 0.48 and 11%, with a small energy cost for increasing outside air rates with heat recovery, or 25–50% energy savings for natural ventila- tion and mixed-mode conditioning (e.g., Fisk and Rosenfeld 1997; Kroeling et al. 1988). Healthy, sustainable thermal control. This second component depends on commitments to separate ventilation air from thermal condi- tioning, design for dynamic thermal zone size, provide individual thermal controls (e.g., underfloor air), design for building load balanc- ing and radiant comfort, and engineer proto- typed, robust systems. International case studies demonstrate that providing individual tempera- ture control for each worker increases individ-
  • 12. ual productivity by 0.2–3% and reduces sick building syndrome (SBS) symptoms and absen- teeism, while saving 25% of conditioning energy (e.g., Wyon 1996). Healthy, sustainable light. The third com- ponent can be achieved by maximizing the use of daylight without glare, selecting the highest quality lighting fixtures, separating task and ambient light, and designing plug-and-play lighting with dynamic lighting zones. Case stud- ies demonstrate that improved lighting design increases individual productivity between 0.7 and 23%, reduces headaches and SBS symp- toms by 10–25%, while reducing annual energy loads by 27–88% (Heschong et al. 2002). Workplace ergonomics and environmental quality. Improving this fourth component has, as its goals, the well-being and efficiency of indi- vidual workers with energy-efficient technolo- gies; optimal lighting, temperature, and placement of furniture; and healthy interior materials. Sustainable design depends on the use of materials that support healthy environments while reducing transportation energies that carry secondary health concerns. Material selection is critical to thermal performance, air quality and outgassing, toxicity in fires, cancer-causing fibers, and mold, all which affect respiratory and digestive systems, eyes, and skin (Dainoff 1990). Access to the natural environment. The fifth component is achieved by providing individual access to nature by maximizing the use of day-
  • 13. light without glare, maximizing the use of nat- ural ventilation with mixed-mode HVAC, and designing for passive solar heating and cooling. Access to the natural environment may increase individual productivity between 0.4 and 18% and reduce absenteeism, SBS, and recovery time while saving even 40% of lighting energy (Center for Building Performance and Diagnostics/Advanced Building Systems Integration Consortium 2005). Land use and transportation. This last component can be improved by commitments to designing mixed-use communities, allowing for multigenerational mobility with mixed- mode transportation, and preserving and cele- brating natural landscapes. For land use, walkable neighborhoods may contribute to prevention of obesity (Srinivasan et al. 2003). Cool roofs and cool community developments with increases in landscaped surfaces and tree canopies demonstrated reductions in annual cooling loads by 10%, peak cooling by 5%, as well as benefits for carbon sequestration, storm runoff management, and a 6–8% reduction in smog that could potentially reduce respiratory illnesses (Rosenfeld and Romm 1997). Quantifying the Value of the Built Environment to Health It is imperative to incorporate the full life-cycle costs of a poor-quality built environment, from materials to systems to land use and transporta- tion. Based on health insurance costs reported in five references by independent nonprofit organizations, human resource research firms,
  • 14. and the U.S. government, the average employer cost for health insurance was approximately US$5,000 per employee per year in 2003 (Figure 1). Some health conditions and illnesses have been linked to the quality of the indoor environment, including colds, headaches, respi- ratory illnesses, musculoskeletal disorders, back pain, and symptoms of SBS. These are pre- sented in Figure 1 with references. Suboptimal indoor environments can lead to a variety of adverse health effects that result directly in increased physician visits and medical treatment. This leads to increases in health insurance costs, both for institutions and for individuals. Improvements in indoor environ- ments, such as increased ventilation rates, better ergonomics and lighting, and improved heating and cooling methods, would reduce many of the adverse symptoms and illnesses described above. Human health in the built environment is one of the most critically needed research efforts, requiring both extensive experimental and field research. Controlled laboratory experiments Loftness et al. 966 VOLUME 115 | NUMBER 6 | June 2007 • Environmental Health Perspectives $ P er p
  • 16. Energys,t ($450) Rent/mortgageq,r ($3,200) Technology ($10,000) Benefitsa,b ($18,500) Salarya,b ($45,000) Potential benefits of quality buildings $5,300 Turnoveri,j $765 (1.7%) Absenteeismk Worktime loss $5,000 Healthc–g $244 Lower respiratoryl $101 Asthmam $95 Allergiesm $92 Back painn $73 Headachesm $68 Coldo $17 MSDp $19 Throat irritationm $18 Eye irritationm $18 Sinus conditionsm
  • 17. $1,000 Connectivity (Forrester Group) $226 Interior systems $70 Utility central systems $62 Roads and grounds $36 External building $73 Process and environmental systems 12.5% Productivityh Figure 1. Improving the quality of the built environment will reduce the life cycle costs of business. Monetary amounts are in U.S. dollars per year. MSD, musculoskeletal disorders. Forrrester Group is part of Forrester Research (Cambridge, MA). Data from aU.S. Department of Labor (DOL) (2004a); bU.S. DOL (2004b); cU.S. DOL (2002); dKaiser Family Foundation and Health Research and Educational Trust (2003); eTowers Perrin HR Services (2003); fU.S. Chamber of Commerce (2003); gDeloitte & Touche (2003); hLeaman (2001); iU.S. DOL (2003b); jFitz-Enz (2000); kU.S. DOL (2003a); lBirnbaum et al. (2003); mU.S. EPA (1998); nGuo et al. (1999); oFendrick et al. (2003); pSilverstein et al. (2000); qGeneral Services Administration (2003); rInternational Facility Management Association (IFMA) (2002); sU.S. DOE (1998); tU.S. Department of Energy (DOE) (2004); uIFMA (2001).
  • 18. need to be carried out simultaneously with experiments in actual buildings to map chains of consequence and to identify possible building- related causes for the rise in respiratory prob- lems, fatigue, stress, depression and other health-related declines in the quality of life. Yet there is remarkably little federal investment in defining and valuing healthy buildings and communities (Figure 2). The opportunity to substantially improve the health of building and community resi- dents through investments in higher quality materials, systems, and land-use planning is significant. The catalyst for these investments must be research and subsequent policy based on the combined expertise of the health research community and the sustainable design and engineering disciplines that we hold responsible for our built environment. Human Influence on Healthy Indoor Air Humans have a major role in maintaining the quality of the indoor environments in which they live. Lifestyles that affect IEQ include the following: • Personal cleaning habits. Examples include frequency of vacuuming and washing of bed linen and towels. • Other personal behavior such as whether kitchen or bathroom fans are commonly used and whether windows are opened to increase air circulation if certain consumer products
  • 19. are used. • The types of consumer products that are pur- chased and where and how the consumer and other occupants of the residence use them. • Decisions about the types of house or apart- ment furnishings that are purchased, for example, the presence of carpets and curtains in various rooms, and remodeling choices. • Decisions about the types of appliances that are purchased, for example, a central air cleaning system or a high-efficiency vacuum cleaner. • Personal cleaning habits. Examples of the sources of indoor pollu- tants such as lead, pesticides, polycyclic aro- matic hydrocarbons (PAHs), allergens, and volatile organic compounds (VOCs) include consumer products, the dust present in carpets and furniture, household pets, or pollutants entering the house from outside air. The accu- mulation of dust, dust mites, and tracked-in soil in old carpets, sofas, and mattresses appears to be a major source of exposure to lead, pesti- cides, allergens, PAHs, and VOCs and can be affected by cleaning habits such as the fre- quency of vacuuming and the washing of bed linen and towels (Roberts and Dickey 1995). Other personal behaviors in indoor environ- ments. Personal behaviors such as opening win- dows and using exhaust fans can have significant
  • 20. impacts on reducing exposures from activities such as paint stripping (Riley et al. 2000). Window-opening behaviors can have a strong effect on a home’s air change rate; thus, this fac- tor should be incorporated into exposure analy- ses when estimating human exposure to indoor air pollutants (Howard-Reed et al. 2002). Behaviors related to heating and cooling the building can also affect the air-exchange rate and the prevalence of microbial and chemical contaminants (Flannigan and Miller 2001). Common household water-use activities such as showering, clotheswashing, handwashing, bathing, dishwashing, and indirect shower expo- sure can increase indoor chemical exposures by inhalation of vaporized or aerosolized chemicals and by inadvertent ingestion of water. For example, some of the greatest increases in sys- temic exposure to trihalomethanes (THM) have been associated with showering (direct and indi- rect), bathing, and hand dishwashing (McKone 2005; Nuckols et al. 2005). Activities such as cooking, arts and crafts, cleaning floors, and painting can contribute to short-term increases in indoor VOC levels. Diminished VOC levels were achieved by turning on the air-condition- ing system (Clobes et al. 1992). Activities shown to generate considerable amounts of indoor par- ticulate matter include cooking, smoking, clean- ing, sources such as cigarette side-stream smoke, pure wax candles, scented candles, a vacuum cleaner, an air-freshener spray, a flat iron (with or without steam) on a cotton sheet, electric radiators, and electric and gas stoves (Afshari et al. 2005).
  • 21. A study by Ferro et al. (2004) of the per- sonal, indoor, and outdoor particulate matter (PM) concentrations for a variety of prescribed human activities found that the activities that resulted in the highest exposures to PM with aerodynamic diameters ≥ 2.5 µm (PM2.5), ≥ 5 µm (PM5), and ≥ 10 µm (PM10) were those such as dry dusting, folding clothes and blankets, and making beds. Such activities dis- turbed dust reservoirs on furniture and textiles. The vigor of activity and type of flooring were also important factors for dust resuspension. The findings demonstrate that a wide variety of indoor human resuspension activities increases human exposure to PM and contributes to the “personal cloud” effect (Ferro et al. 2004). Consumer products and their use in resi- dences. Various household products can be used alone or together with other products for clean- ing, cosmetics, or a variety of other purposes. Consumer studies have found that there can be large intra- as well as interindividual variation in the frequency, duration, and amount of use of products such as dishwashing detergents, pesti- cides, cleaning products, and hair-styling prod- ucts (Weegels and van Veen 2001). Common household activities can raise exposures to volatile organic chemicals (VOCs) up to a fac- tor of 100 compared with exposures during the sleep period and far above the highest observed outdoor concentrations. Major associations of consumer products with particular indoor chemical exposures include deodorizers and the
  • 22. level of p-dichlorobenzene, dishwasher and laundry detergents and the level of chloroform, smoking and the levels of benzene and styrene, and painting and using paint remover and the levels of n-decane and n-undecane (Wallace et al. 1989). Moreover, combinations of consumer products, or a mix of consumer products with outdoor air, can produce respiratory tract irri- tants. Cleaning agents and air fresheners can contain chemicals that react with other air cont- aminants to yield potentially harmful secondary products. For example, terpenes from consumer products can react with ozone in indoor air to generate secondary pollutants (Clausen et al. 2001; Nazaroff and Weschler 2004). Home furnishings and decorating. Decisions about home furnishings and decoration, such as the types of furniture purchased, the presence of carpets and curtains in various rooms, and remodeling choices, can also affect indoor cont- aminant exposures. For example, the remodel- ing of a residence and the adoption of energy conservation methods can reduce ventilation and increase relative humidity. The changes in these factors could increase the levels of dust, dust mites, molds, VOCs, and other indoor air pollutants (Roberts and Dickey 1995). Household appliances. Decisions about the types of appliances that are purchased can be driven partly by personal cleaning habits, for example, how clean the residence is kept. Further, using air-conditioning while sleeping
  • 23. can lead to a considerable build-up in the room of carbon dioxide (CO2) from all types of air- conditioning systems. These CO2 levels were substantially higher than the levels in naturally ventilated bedrooms. A survey was conducted to investigate whether the occupants exhibited Healthy building design Environmental Health Perspectives • VOLUME 115 | NUMBER 6 | June 2007 967 Figure 2. U.S. government investments (US$) in research to achieve healthy indoor environments (Office of Management and Budget 1998). Abbreviations: DOE, Department of Energy; EH, envi- ronmental health; EPA, U.S. Environmental Protection Agency; GSA, General Services Administration; NIH, National Institutes Health; NSF, National Science Foundation. Blue bars, total U.S. federal research funding; black bars, U.S. built environment research funding; GSA white bar, total construction dollars, not total research dollars; NIH white bar, environ- mental health research funding but not directly built environment research funding. B il li on s of U
  • 24. S $ in R & D 18 16 14 12 10 8 6 4 2 0 DOE NIH GSA EPA NSF $17 $11.6 $0.35 $0.42 $0.01
  • 25. $7 $3 $11 in construction $0.58 in EH $0.04 symptoms of SBS while sleeping in air-condi- tioned as well as naturally ventilated bedrooms. Almost all occupants who used air-conditioning while sleeping exhibited one or more SBS symp- toms and usually displayed more SBS symptoms after using air-conditioning than when they used natural ventilation. The survey also revealed that the frequency and duration of using air-conditioning has an important impact on the exhibition of the SBS symptoms (Wong and Huang 2004). Ongoing Developments in Controlling Emissions from Products and Building Materials Today, more consumer products and building materials are being studied and certified as low chemical-emitting products and materials to serve as primary control measures for achieving good indoor air quality. Key products identified by the U.S. Environmental Protection Agency
  • 26. (EPA) as sources of indoor air pollution are office furniture, flooring, paints and coatings, adhesives and sealants, wall coverings, office equipment, wood products, textiles, insulation, and cleaning products. Product emission testing protocols have been designed to help ensure that the test results can be translated into real- world product usage scenarios. The American Society for Testing Materials (ASTM) has established guidelines for measur- ing chemical emissions using environmental chambers. ASTM D5116-97 (ASTM 2007a) and D6670-01 (ASTM 2007b) are the founda- tion for some product-specific test protocols. One testing laboratory, the Greenguard Environmental Institute (GEI) in Atlanta, Georgia, has established performance-based standards to label goods with low chemical and particle emissions for use indoors, primarily building materials, interior furnishings, furni- ture, cleaning and maintenance products, elec- tronic equipment, and personal care products. The standards of GEI establish certification procedures, including test methods, allowable emissions levels, product sample collection and handling, testing type and frequency, and pro- gram application processes and acceptance (GEI 2005). The Carpet and Rug Institute’s “Green Label” Testing Program for Carpets and Vacuum Cleaners in Dalton, Georgia, is another example of testing and certification of low-emitting products (Carpet and Rug Institute 2005). “Smart” construction materials and coatings
  • 27. are being developed through a test program for innovative construction materials, with the goal of decreasing indoor air pollution. One example is the PICADA (Photo-catalytic Innovative Coverings Applications for De-Pollution Assessment) project, involving a European con- sortium of private enterprises, research institu- tions, and the European Commission’s Joint Research Centre. The “smart” construction materials (plaster, mortar, architectural concrete) and coatings contain titanium dioxide (TiO2). Nitrogen oxide (NOx) gases and organic com- pounds diffuse through the porous surface of the materials and coatings and stick to the TiO2 nanoparticles. Absorption of ultraviolet light by the TiO2 leads to its photoactivation and the subsequent degradation of the pollutants adsorbed onto the particles. The acidic products created by this process are washed away by rain and/or neutralized by alkaline calcium carbonate contained in the materials. Such new construc- tion materials could help to reduce levels of NOx gases that cause respiratory problems and trigger smog production, and of other toxic sub- stances such as benzene. Tests with photocatalytic materials under field conditions have shown that outdoor air quality can be significantly improved. For example, up to 60% reduction in the concen- tration of NOx at street level was detected after 7,000 m2 of road surface in Milan, Italy, were covered with a photocatalytic cementlike mate- rial. Such new construction materials and coat- ings could play a major role in helping meet the
  • 28. European Union (EU) target of reducing NOx levels to < 21 ppb/year by 2010. Although EU researchers have focused on the development of these types of materials for outdoor applica- tions, future work is planned to determine whether these products can also be used as depolluting building materials and coatings in indoor environments (PICADA 2005). Fungal Resistance of Construction Materials and Finishes Dampness, moisture, and mold problems in buildings are a major factor affecting the quality of indoor air worldwide [Institute of Medicine (IOM) 2004]. These phenomena have a well- documented link to health effects such as respi- ratory symptoms and asthma (Bornehag et al. 2001, 2004; IOM 2004; Peat et al. 1998). Various signs of dampness or moisture damage are common in modern buildings (Nevalainen et al. 1998), and the prevalence of observations of mold varies from 1.5–20% (Bornehag et al. 2005; Anonymous 1993). Dampness and mold are complex problems both from the point of view of building con- struction and human health. Although fungal spores are present everywhere, it is when damp- ness and moisture are uncontrolled that fungi grow and thus develop into visible mold. Use of fungicides or disinfection products do not solve the problem and may even be an additional load to indoor chemical exposures. Moisture control may be difficult to manage in existing buildings, and therefore any delay in the devel-
  • 29. opment of actual mold damage allows time for drying of the moistened materials. It is evident that the materials of a healthy building should be sturdy and resistant to microbial growth. It is also evident that both dissemination of infor- mation and access to training about the risks of dampness and mold are necessary for control of the problem. Training should be directed to professionals in building design and construc- tion as well as in building maintenance, man- agement, and renovation. Furthermore, the general public, as the users and occupants of buildings, plays an important role in prevention and control of these problems. Therefore, their awareness of the risks of dampness and inter- ventions to control it is critical. Adan (1994) found that the finishing mate- rials on buildings play a pivotal role in mold growth and the quality of the indoor environ- ment. Effects are most pronounced in places with highly transient moisture loads such as bathrooms. Regardless of insulation levels and even with high ventilation rates, moistening of surfaces cannot be avoided. Moisture retention in the finish may cause sustained high surface humidity, even when the indoor air is dry. This explains why, in modern highly insulated dwellings in cold and temperate maritime cli- mates, mold risk is primarily a matter of mater- ial properties. Considering the industrial trend toward ecofriendlier products, which is gener- ally accompanied by an increase in constituent biodegradability, the situation is growing worse.
  • 30. Therefore, a sustained strategy of indoor fungal growth control must consider the piv- otal role of finishing products. Two major developments are promising: • Research and development is under way in the supply industry, with the goal of reduced material susceptibility. This initiative is driven primarily by environmental legislation and concerns biocides in particular. • Performance requirements in building codes and/or consumer-oriented product labeling are being considered for finishes. The finish- ing materials very often are a designer’s or consumer’s choice. Labeling can make the end-user conscious of the consequences. Reducing biosusceptibility. Presently, suffi- cient resistance of materials to microbial attack requires addition of biocides, with paints being the main application area. There are two major technical limitations in terms of release and environmental impact. First, the activity period of the biocide is usu- ally much shorter (maximum 1–2 years) than the desired service life of the finish, leading to early replacement. Biocides tend to leach out quickly in the early stages of the coating’s lifespan, thereby decreasing the amount of active material available for the longer term. Raising initial bio- cide concentrations tries to counter this effect. Biocides must be sufficiently mobile to find their way to the surface. Consequently, biocides are inherently sensitive to leaching, especially
  • 31. when the surface is in direct contact with water. To prolong the effective release period, a viable approach is to incorporate a retarding step Loftness et al. 968 VOLUME 115 | NUMBER 6 | June 2007 • Environmental Health Perspectives before the diffusion of the biocide to the surface occurs. A number of such approaches have been introduced. Most are based on reservoir proper- ties of added porous materials such as zeolites and silica (e.g., Edge et al. 2001). Other release- concepts are emerging, addressing release-on- demand (inclusion of nanopackages), slow release, and so-called bioswitches, which have been applied successfully in other areas such as medical applications and food packaging. Second, most traditional biocides, for example, mercury compounds, are or will soon be under prohibitive rules. In this context, the EU Biocides Directive 98/8/EC (European Parliament and the Council of the EU 1998) reflects a tightened environmental policy. Therefore, European industries are eagerly searching for ecofriendlier alternatives. Toward performance requirements and product labeling. The recognition of the crucial role of the interior finish calls for an approved method for assessing the its mold control per-
  • 32. formance. Such a method is a basic instrument for product labeling and end-user implementa- tion. In addition, control of fungal growth on materials has been identified as a priority in EU member states responding to mandate M/366 (approved November 2004; EU Commission 2005c). The CPD applies to all construction products that are produced for or incorporated within building and civil engineering construc- tion works. It harmonizes all construction products subject to regulatory controls for marking purposes. Present methods use a single moisture regime and do not explicitly consider effects of transient moisture loads and subsequent mater- ial performance in relation to the transient loads. Most tests are based either on a more or less steady-state level of the relative humidity below saturation (Anonymous 1968, 1975, 1978, 1986, 1988a) or unambiguous surface moisten- ing (Anonymous 1988b, 1989a, 1989b). Adan et al. (1999) proposed a new test that considers the effect of indoor climate dynamics. Pilot application of the test during the past decade yielded a highly reproducible and dis- criminating picture of material performance in terms of fungal resistance and showed perfor- mance that might differ considerably based on the moisture load. Tests were conducted specifi- cally on silicon caulking typically applied in san- itary rooms (Adan and Lurkin 1997a); a wide range of coating types including waterborne interior paints (Adan et al. 1999); specialties
  • 33. such as high-absorbing claddings (Adan and Lurkin 1997b) and ceramic coatings (Sanders 2002a); fiber products, gypsum-based plasters, and wallpapers including glues (Adan et al. 1999); and cement-based panels (Sanders 2002b). Fungal resistance was found to be a product-based feature and application oriented, emphasizing the importance of indoor climate dynamics for mold resistance. These findings laid the foundation for an approved product qualification system in the Netherlands with respect to fungal resistance. Such a system is a step toward performance requirements in build- ing regulations. Moreover, product labeling pro- vides support to end users, i.e., tenants and building owners, the actual occupants. Labeling is defined by a three-level classifi- cation system: I, resistant; II, fairly resistant; and III, sensitive (Table 1). These definitions are based on analysis of the entire growth pat- tern as a function of time (Adan 1995; Adan et al. 1999). The basic principle underlying the classifi- cation system is the potential of most products to exhibit widely divergent behavior as a func- tion of the moisture load. In the past decade, in about 50% of the tested products, steady-state and transient (i.e., condensation) conditions showed highly differing behavior, underlining the importance of considering both climatic conditions in assessing product performance. Consequently, a labeling system should be con- nected to a recommended application. The best quality (labeled “I”) in terms of resistance
  • 34. reflects that the majority of mold problems occurs in indoor areas with a distinct vapor pro- duction [e.g., bathrooms and kitchens in 60 and 40% of cases in the Netherlands, respec- tively (Anonymous 1993)]. In all other indoor areas, with a more or less steady-state indoor humidity, risks of surface growth are a conse- quence of interaction of finishing product, building construction—thermal bridging in particular—and average humidity or ventila- tion. In these cases, product labeling discrimi- nates between fairly resistant products that can be applied on thermal bridges and sensitive products that should be applied only on inner constructions in dry environments. Conclusions We discussed the issue of how to design a healthy building from three viewpoints. The first approach describes sustainable develop- ment, focusing on what should be considered in design and land use. Second, the analysis of how occupants affect their indoor air quality links the everyday use of the building to its design. Third, the overview of recent develop- ments in products and materials and their cer- tification and labeling indicates a trend toward addressing current problems. Sustainable design rediscovers the social, environmental and technical values of pedes- trian, mixed-use communities, using existing infrastructures, including main streets and small-town planning principles, and recaptur-
  • 35. ing indoor–outdoor relationships. Sustainable design introduces benign, nonpolluting materi- als and assemblies with lower energy require- ments and higher durability and recyclability. Humans have a major role in maintaining the healthy indoor environment, especially in residences. This role includes personal cleaning habits and other personal behaviors. The occu- pants of the building decide the types of con- sumer products to be used and furnishings and appliances to be purchased, as well as where and how they are used. Thus, the occupant has a key role in determining the quality of indoor air in his/her residence. Certification of consumer products and building materials as low-emitting products is a primary control measure for achieving good indoor air quality. Key products in this respect are office furniture, flooring, paints and coat- ings, adhesives and sealants, wall coverings, wood products, textiles, insulation, and clean- ing products. The finishing materials have a key role in moisture retention and mold growth. The goal of product development is to reduce material susceptibility, to establish performance requirements for finishes in building codes and to require consumer-oriented product labeling. Training professionals in various fields of design, construction, maintenance, and man- agement of the building is necessary in devel- oping healthier environments for living and work. Dissemination of information concern- ing the healthiness of the indoor environment
  • 36. and what a consumer can do about it is essen- tial to increase root-level activities toward obtaining and maintaining healthier buildings. REFERENCES Adan OCG. 1994. On the Fungal Defacement of Interior Finishes [PhD Thesis]. Eindhoven, the Netherlands:Eindhoven University of Technology. Adan OCG. 1995. Response of fungi to transient relative humidi- ties. In: Proceedings of the International Symposium on Moisture Problems in Building Walls, 11–13 September 1995, Porto, Portugal, 62–74. Adan OCG, Lurkin JHM. 1997a. The fungal resistance of Dutch sil- icon caulking. In: Proceedings of the CIB-W40 Meeting, 7–10 October 1997, Kyoto, Japan. Rotterdam, the Netherlands: CIB, 1–10. Adan OCG, Lurkin JHM. 1997b. The Fungal Sensitivity of Three Types of Condensate Absorbent Cladding ‘Firet CondenStop’. Report 97-BT-R1222. Delft, the Netherlands: TNO Building and Construction Research. Healthy building design Environmental Health Perspectives • VOLUME 115 | NUMBER 6 | June 2007 969 Table 1. The Dutch classification system for fungal resistance of interior finishes.
  • 37. Class Quality Recommended application I Resistant Indoor environments with transient moisture loads such as bathrooms, kitchens, production processes, swimming pools II Fairly resistant All other indoor areas, with a more or less steady-state indoor humidity, such as living rooms, attics, storage rooms, or depots III Sensitive Only on inner constructions not being part of the building envelope in environments other than class I Adapted from Adan et al. (1999). Loftness et al. 970 VOLUME 115 | NUMBER 6 | June 2007 • Environmental Health Perspectives Adan OCG, Lurkin JHM, Van der Wel GK. 1999. De schimmel- gevoeligheid van afwerkmaterialen [in Dutch]. Report 1999- BT-MK-R0205-02. Delft, the Netherlands:TNO Building and Construction Research. Afshari A, Matson U, Ekberg, LE. 2005. Characterization of indoor sources of fine and ultrafine particles: a study conducted in a full-scale chamber. Indoor Air 15:141–150. Anonymous. 1968. BS 1982. Methods of Test for Fungal Resist- ance of Manufactured Building Materials Made of, or
  • 38. Containing, Materials of Organic Origin. London:British Standards Institution. Anonymous. 1975. Designation G 21-70 (Reapproved 1975). Standard Recommended Practice for Determining Resist- ance of Synthetic Polymeric Materials to Fungi. Consho- hocken, PA:American Society for Testing Materials, 860–863. Anonymous. 1978. ISO 846. Plastics—Determination of Behaviour Under the Action of Fungi and Bacteria—Evaluation by Visual Examination or Measurement of Change in Mass or Physical Properties. Geneva:International Organization for Standardization. Anonymous. 1986. Designation D 3273-86. Standard Test Method for Resistance to Growth of Mold on the Surface of Interior Coatings in an Environmental Chamber. Conshohocken, PA:American Society of Testing Materials, 596–599. Anonymous. 1988a. IEC Publication 68-2-10. 1988. Basic Environmental Testing Procedures. Part 2: Tests- Test J and Guidance: Mould Growth. Geneva:International Electro- technical Commission. Anonymous. 1988b. Test Methods Manual, no. 2.6.1. Fungus Resistance Printed Wiring Materials. Bannockburn, IL:Institute for Interconnecting and Packaging Electronic Circuits. Anonymous. 1989a. BS 3900. British Standard Methods of Tests for Paints, Part G6. Assessment of Resistance to Fungal Growth. London:British Standard Institution. Anonymous. 1989b. ML-STD-810F. Environmental Engineering
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  • 48. Real Estate Principles A Value Approach Fifth Edition Chapter 4 Government Controls and Real Estate Markets © McGraw-Hill Education. All rights reserved. Authorized only for instructor use in the classroom. No reproduction or further distribution permitted without the prior written consent of McGraw-Hill Education. Limits on OwnershipRestrictions of UseSeparation of Use or PossessionComplete RemovalShare of ValuePrivateDeed Restrictions/ HOA or Condo BylawsEasements & LeasesLiens (In default)________GovernmentRegulation through Police Power_______Eminent DomainTaxation This chapter examines the government limitations on real property ownership © McGraw-Hill Education. 4-‹#› Land use is one of the most regulated activities in our society. Why? Must it be this way? © McGraw-Hill Education.
  • 49. 4-‹#› Features of Real Estate that Cause Market Distortions “Spillover” effects from nearby land uses Uniqueness of location (absolute monopoly) Unknown quality or condition of existing structures Instability of land uses around residential neighborhoods © McGraw-Hill Education. 4-‹#› Resulting Market Failures in Real Estate (1 of 2) Monopoly Utilities as “natural” monopolies “Holdouts” in land assembly efforts (roads, other public uses) Incomplete information Construction quality hidden Buyers unable to judge natural risks Hurricanes Earthquakes Fires © McGraw-Hill Education. 4-‹#› Resulting Market Failures in Real Estate (2 of 2) Buyers unable to judge adequacy of structure quality Wind tolerance Resilience against shocks Fire safety and resistance © McGraw-Hill Education. 4-‹#›
  • 50. More Market Failures (1 of 2) Externalities “Spillover” effects of land use for which initiator is not held accountable Traffic congestion Storm runoff Emissions (smoke, gases, particles, noise, light) Urban sprawl Disorderly extension of urban infrastructure © McGraw-Hill Education. 4-‹#› More Market Failures (2 of 2) Uncertainty of residential values Effect of non-conventional structures Effect of nonresidential land uses Effect of non-conventional population –e.g., students © McGraw-Hill Education. 4-‹#› The “Revolution” in Land Use Controls Pre-1970: Little interest in land use controls No land use plans had force of law Zoning very limited in function Focused on protection of single-family homes Did not exist in many areas Environmental movement of late 1960s Rachael Carson: Silent Spring Love Canal Notion of “spaceship earth”
  • 51. © McGraw-Hill Education. 4-‹#› Some Critical Questions Will land use planning solve market failures? At what level should control be imposed? For subdivisions? For streets and utilities? For schools? For water resources and drainage control? For transportation systems? For rivers and wetlands? For ecological and endangered species? © McGraw-Hill Education. 4-‹#› Is Comprehensive Planning the Answer? What Is Required? Project future population growth Determine requirements for water and waste disposal Project needs for public services (utilities, streets, schools, parks and recreation, safety) Projected demand for various land uses (public, residential, nonresidential) Design compatible arrangement of needed land uses (land use map) © McGraw-Hill Education. 4-‹#› Challenges to Comprehensive Planning Changing notion of “best practice” Cul-de-sacs or grid streets?
  • 52. Mixed density and mixed use or containment of nonresidential use? How much mass transit? Limited actual experience to rely on (little more than 30 years) Insufficient theory and information Inability to foresee the future well © McGraw-Hill Education. 4-‹#› Traditional Planning versus New Urban Planning (1 of 2) Traditional Separated uses Automobile oriented Priority placed on easy ingress and egress Uniform density Cul-de-sac hierarchy in neighborhoods © McGraw-Hill Education. 4-‹#› Traditional Planning versus New Urban Planning (2 of 2) New Urban Mixed use Public transportation Pedestrian oriented Sidewalks Houses close to street Rear alleys Grid streets with restricted traffic flows © McGraw-Hill Education. 4-‹#›
  • 53. Traditional Land Use Controls: Building Codes Older than zoning (circa 1900) Issues of safety Fire: Materials, alarms, electrical and gas systems Sanitation: Plumbing, water, and HVAC requirements Injury: Design and strength Continue to evolve Effect of Hurricane Andrew, 2004-5 hurricanes, Katrina New technology (e.g., smoke detectors) Changing perception of needs (e.g., bedroom windows large enough to step through) © McGraw-Hill Education. 4-‹#› Traditional Land Use Controls: Zoning Features of traditional zoning Use classifications: Residential, commercial, industrial, automotive Use districts (zoning map) Setback requirements (side, front and back) “Bulk” or density limits (minimum lot size, height limits, maximum floor area ratios) Special use districts: Service stations, hospitals, churches, private schools, cemeteries © McGraw-Hill Education. 4-‹#› Traditional Land Use Controls: Subdivision Regulations Features of subdivision regulations Standards for streets, sewers, and water systems Adequate water supply for fire safety
  • 54. Adequate drainage and run-off retention Open spaces Lot layout Easements for utilities Traffic and pedestrian safety © McGraw-Hill Education. 4-‹#› Traditional Land Use Controls: Planning and Zoning Administration (1 of 2) Planning and Zoning Commission created in the zoning ordinance Appointed by elected officials Ultimately is advisory to elected officials Oversees implementation of the ordinance Considers requests for specific changes Requested changes must: © McGraw-Hill Education. 4-‹#› Traditional Land Use Controls: Planning and Zoning Administration (2 of 2) Be compatible with a comprehensive plan Be justified if they require change in the comprehensive plan Not have undue effect on surrounding land uses or the community © McGraw-Hill Education. 4-‹#› Traditional Land Use Controls: Board of Adjustment
  • 55. Required in zoning ordinance Appointed by elected officials Reviews petitions for variances Decisions are final rather than advisory to the elected officials Only appeal is through the courts © McGraw-Hill Education. 4-‹#› Traditional Land Use Controls: Site Plan Review May be the same as planning and zoning commission Review subdivisions and most other building site plans Public review (neighbors and others) Public offices (public safety - fire, police, emergency vehicles; utility officials; school officials) Informal procedure allows criteria and rules to change with public pressure Most “treacherous” step for proposed new development? © McGraw-Hill Education. 4-‹#› Zoning Issues and Concepts (1 of 2) Legality of zoning established by USSC: Village of Euclid versus Ambler Realty - 1926 Nonconforming use: Use conflicting with zoning map, but existing prior to its enactment Cannot be substantially changed Must be continuous Can be “amortized” away (e.g., billboards) © McGraw-Hill Education. 4-‹#›
  • 56. Zoning Issues and Concepts (2 of 2) Variance: Exception to requirements granted due to hardship Common example: wavier of setback requirement Exclusionary zoning (unreasonable lot size; inadequate provision for low- and moderate-income housing) © McGraw-Hill Education. 4-‹#› Do Land Use Controls Solve the Problem of Market Failure? Does zoning raise the cost of “threshold” housing unnecessarily? Does it interfere with economically efficient land use patterns? Example: Does zoning make neighborhood services excessively remote? Does low density resulting from zoning contribute to urban sprawl? Houston: effective land uses without zoning? © McGraw-Hill Education. 4-‹#› Newer Approaches to Land Use Control: Planned Unit Development Detailed development plan negotiated with authorities Mixed use Mixed density No standard setback requirements Open community spaces Community recreation and other facilities © McGraw-Hill Education.
  • 57. 4-‹#› Newer Approaches to Land Use Controls: Performance Standards Storm runoff limits Noise and emission limits Traffic impact limits Tree removal restrictions © McGraw-Hill Education. 4-‹#› More New Land Use Controls Impact fees Favorite of economists (in principle) Despised by many in the building community Appear to be used more as revenue source than tool to guide land use Growth restrictions Temporary moratoriums US Supreme Court refuses to review Petaluma, Ca. limit on the number of new housing units. Also Boulder, Co., and Boca Raton, Fl. © McGraw-Hill Education. 4-‹#› Another Way? Form Based Zoning Land uses are determined not by prescription but “organically” based on: Development density Street character Parking arrangements Walkway character
  • 58. Structure shapes and sizes Foliage character © McGraw-Hill Education. 4-‹#› How Form-Based Zoning Works (1 of 2) Within broad categories, land uses can go anywhere Households will select a form that suites their location, household and lifestyle preference: rural, suburb, urban core Non-residential uses will select as their business requires: © McGraw-Hill Education. 4-‹#› How Form Based Zoning Works (2 of 2) Neighborhood shops versus large urban stores Small local offices versus financial centers Example: Denver, Colorado http://formbasedcodes.org/codes/denver-commons/ © McGraw-Hill Education. 4-‹#› Spaceship Earth? What are other effects of the “spaceship earth” scenario? © McGraw-Hill Education. 4-‹#› Sample of Environmental Controls since the Late 1960s Clean Air Act
  • 59. Clean Water Act Comprehensive Environmental Response Compensation and Liability Act (CERCLA) Occupational Safety and Health Act (OSHA) Endangered Species Act Increasing limitations on “fracking” © McGraw-Hill Education. 4-‹#› Some Hazardous Materials Asbestos and fiberglass PCBs Leaking underground storage tanks (LUSTs) Radon Mold © McGraw-Hill Education. 4-‹#› Is there a limit to regulation? Pennsylvania Coal Company v Mahon (US Supreme Court, 1922): Courts must balance public safety and welfare against taking of property At some point eminent domain must be used. (Murr v. Wisconsin now before USSC) Minority opinion in the case: “We are in danger of forgetting that a strong public desire to improve the public condition is not enough to warrant achieving the desire by a shorter cut than the constitutional way of paying for it.” © McGraw-Hill Education.
  • 60. 4-‹#› Power of Eminent Domain Eminent domain: Right of government to acquire private land, without the owner’s consent, for public use, with due process and just compensation Condemnation: Legal procedure for exercising the right of eminent domain Public use versus public purpose Just compensation based on highest and best use Problems of excessive use Inverse condemnation © McGraw-Hill Education. 4-‹#› Eminent Domain Controversy - I Concept of “public use” expanded to “public purpose” US Supreme Court in 1954 allowed condemnation of “blighted areas” for private redevelopment Michigan Supreme Court in 1981 allowed condemnation to enable GM manufacturing facilities Wide-spread subsequent condemnation of “blighted areas” for private redevelopment Driven by local government hunger for an increased property tax base © McGraw-Hill Education. 4-‹#› Eminent Domain Controversy – II Kelo v. New London Ct., 2005 U.S. Supreme Court allowed use of eminent domain to obtain non-blighted property for private redevelopment
  • 61. Left it to states to decide whether to intervene Most states initiated legislation to limit use of eminent domain Congress enacted law to prevent application of Federal monies for such use Most states moderated the proposed laws to limit eminent domain http://www.youtube.com/watch?v=4N1svadJQ40 © McGraw-Hill Education. 4-‹#› A Larger Perspective on “Kelo” (1 of 2) New London, Ct., had been long recognized as an abandoned and depressed community. A community/state plan of redevelopment had evolved, with subsidies from the state. Achievement of the plan required removal of all of the houses in the Kelo area. © McGraw-Hill Education. 4-‹#› A Larger Perspective on “Kelo” (2 of 2) “Kelo” can hardly be viewed as an isolated or arbitrary taking. Greatest significance of the USSC “Kelo” decision?- Shift of authority back to the states. © McGraw-Hill Education. 4-‹#› The Effect of Property Taxes on Real Estate Can property taxes reduce property values and property wealth? Can an efficient property tax enhance property values and
  • 62. property wealth by the services it funds? © McGraw-Hill Education. 4-‹#› Property Taxes A primary source of local government revenue Reliable and countercyclical Many taxing authorities City Improvement districts County Transportation authorities Schools Water management districts © McGraw-Hill Education. 4-‹#› Property Exempt from Taxes Religious organizations State Property Nonprofit organizations Homestead Educational institutions © McGraw-Hill Education. 4-‹#› Determination of Tax Rate
  • 63. © McGraw-Hill Education. 4-‹#› Computing Tax LiabilityMarket value$150,000Assessed value135,000 = (0.90 × MV)Less: exemptions25,000Taxable value$110,000 Property Tax CalculationTaxing AuthorityMillage RateTaxes LeviedCounty8.58$ 943.80City3.20352.00School district9.861,084.60Water mgt. district0.055.50Total21.692,385.90 © McGraw-Hill Education. 4-‹#› Special Assessments Special assessments: Taxes for specific public improvements affecting a property Street, sewer, etc. Usually charged on a per front foot basis Example: Street improvements of $500 per running foot of street For lot with 100 feet of frontage: 100 × .5 × $500 = $25,000 © McGraw-Hill Education. 4-‹#› Special Assessments and Community Development Districts Many large subdivisions have private community development districts Create and maintain neighborhood infrastructure Utilities Drainage and water retention
  • 64. Streets, bikeways, walkways Recreation facilities Issue tax-exempt bonds and impose property assessments to pay the obligations Have the same lien priority as property taxes © McGraw-Hill Education. 4-‹#› An Example CDD Community in Florida: The Villages Retirement community in north-central FL 10 CDDs provide every community service except criminal law enforcement Population of over 100,000 http://www.thevillages.com/AboutUs/aboutus.htm © McGraw-Hill Education. 4-‹#› Issues with Property Tax Regressive? May be regressive viewed alone Not necessarily regressive if resulting public services also are considered Uneven across geographic areas and property types Distorted by differential protection laws California – Proposition 13 Florida – “Save our Homes” Amendment Poorly administered © McGraw-Hill Education. 4-‹#›
  • 65. Summing up (1 of 2) Land use must be regulated due to market failures The concept of spaceship earth has brought a revolution in land use controls Traditional controls: building codes, zoning, subdivision regulations “Post-revolution” controls: impact fees, performance standards, PUDs, environmental laws © McGraw-Hill Education. 4-‹#› Summing up (2 of 2) When regulation goes too far: eminent domain The problem of expanding use Property taxes as a double-edged sword. Efficient and reliable tax. Can be inequitable and distort land use © McGraw-Hill Education. 4-‹#› End of Presentation © McGraw-Hill Education. All rights reserved. Authorized only for instructor use in the classroom. No reproduction or further distribution permitted without the prior written consent of McGraw-Hill Education. 4-‹#› ( ) ( )
  • 68. T R V V I E R 2/18/2020 Sample Content Topic https://purdueglobal.brightspace.com/d2l/le/content/115680/vie wContent/9224752/View 1/2 Technology and Indoor Environments You read briefly about hazardous materials and gasses, and practiced with environmental vocabulary concerning property sales in the Learning Activity. Now you have an opportunity to do some research and see what technological advances have helped to either eradicate or mitigate the damages done by environmental toxins with regards to real property. Most states have laws pertaining to responsibility for disclosure of such toxins present in homes. The following Course Outcome is assessed in this assignment: GEL-3.04: Examine the relationship between science and technology and the impact on the natural world. Scenario: You are showing clients a house built in 1960 in your state. They are interested in buying the home, but they want to completely remodel it and the mechanical systems
  • 69. including adding a new gas furnace and stove. Research "Healthy Building Materials" in the Purdue Global Library located in the Academic Tools area of the course. Select an article to read and record the title, author, and year. Checklist: What air quality and building materials concerns should they look at regarding the existing home? Analyze possible radon, lead, gas, and asbestos issues and how these affect homeowners and the environment. What scientific discoveries regarding air quality and building materials have led to new technological solutions that will deal with your clients’ potential problems? Based on research on your state’s disclosure statements required of real estate agents, discuss what disclosures of Assignment Details 2/18/2020 Sample Content Topic https://purdueglobal.brightspace.com/d2l/le/content/115680/vie wContent/9224752/View 2/2 hazardous materials the real estate agent or seller is required to make to the buyer of a home in your state. Access the Unit 3 Assignment grading rubric. Respond in a minimum 500–600-word APA formatted and citation styled paper with additional title and reference pages to the Unit 3 Assignment Dropbox before the end of